DIRECTIVE 2010/75/EU OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL
of 24 November 2010
on industrial and livestock rearing emissions (integrated pollution prevention and control)
(Recast)
(Text with EEA relevance)
CHAPTER I
COMMON PROVISIONS
Article 1
Subject matter
This Directive lays down rules on integrated prevention and control of pollution arising from industrial activities.
It also lays down rules designed to prevent or, where that is not practicable, to continuously reduce emissions into air, water and land, to prevent the generation of waste, improve resource efficiency, and to promote the circular economy and decarbonisation, in order to achieve a high level of protection of human health and the environment taken as a whole.
Article 2
Scope
Article 3
Definitions
For the purposes of this Directive the following definitions shall apply:
‘substance’ means any chemical element and its compounds, with the exception of the following substances:
radioactive substances as defined in Article 1 of Council Directive 96/29/Euratom of 13 May 1996 laying down basic safety standards for the protection of the health of workers and the general public against the dangers arising from ionising radiation ( 1 );
genetically modified micro-organisms as defined in Article 2(b) of Directive 2009/41/EC of the European Parliament and the Council of 6 May 2009 on the contained use of genetically modified micro-organisms ( 2 );
genetically modified organisms as defined in point 2 of Article 2 of Directive 2001/18/EC of the European Parliament and of the Council of 12 March 2001 on the deliberate release into the environment of genetically modified organisms ( 3 );
‘pollution’ means the direct or indirect introduction, as a result of human activity, of substances, vibrations, heat, noise or odours into air, water or land, which can be harmful to human health or the quality of the environment, result in damage to material property, or impair or interfere with amenities and other legitimate uses of the environment;
‘installation’ means a stationary technical unit within which one or more activities listed in Annex I, in Annex Ia or in Part 1 of Annex VII are carried out, and any other directly associated activities on the same site which have a technical connection with the activities listed in those Annexes and which could have an effect on emissions and pollution;
‘emission’ means the direct or indirect release of substances, vibrations, heat or noise from individual or diffuse sources in the installation into air, water or land;
‘emission limit value’ means the mass, expressed in terms of certain specific parameters, concentration and/or level of an emission, which may not be exceeded during one or more periods of time;
‘environmental performance limit value’ means a performance value included in a permit, expressed for specified conditions in terms of certain specific parameters;
‘environmental quality standard’ means the set of requirements which must be fulfilled at a given time by a given environment or particular part thereof, as set out in Union law;
‘permit’ means a written authorisation to operate all or part of an installation or combustion plant, waste incineration plant or waste co-incineration plant;
‘general binding rules’ means emission limit values or other conditions, at least at sector level, that are adopted with the intention of being used directly to set permit conditions;
‘substantial change’ means a change in the nature or functioning, or an extension, of an installation or combustion plant, waste incineration plant or waste co-incineration plant which may have significant negative effects on human health or the environment;
‘deep industrial transformation’ means the implementation by industrial operators of emerging techniques or best available techniques involving a major change in the design or technology of all or part of an installation or the replacement of an existing installation by a new installation, which allows an extremely substantial reduction of emissions of greenhouse gases in line with the objective of climate neutrality and optimises environmental co-benefits, at least to the levels that can be achieved by techniques identified in the applicable BAT conclusions, taking into account cross-media effects;
‘best available techniques’ means the most effective and advanced stage in the development of activities and their methods of operation which indicates the practical suitability of particular techniques for providing the basis for emission limit values and other permit conditions designed to prevent and, where that is not practicable, to reduce emissions and the impact on the environment as a whole:
‘techniques’ includes both the technology used and the way in which the installation is designed, built, maintained, operated and decommissioned;
‘available techniques’ means techniques developed on a scale which allows implementation in the relevant industrial sector, under economically and technically viable conditions, taking into consideration the costs and advantages, regardless of whether such techniques are used or produced in the Union, as long as they are reasonably accessible to the operator;
‘best’ means most effective in achieving a high general level of protection of the environment as a whole, including human health and climate protection;
‘BAT reference document’ means a document, resulting from the exchange of information organised pursuant to Article 13, drawn up for defined activities and describing, in particular, applied techniques, present emissions and consumption levels, techniques considered for the determination of best available techniques as well as BAT conclusions and any emerging techniques, giving special consideration to the criteria listed in Annex III;
‘BAT conclusions’ means a document containing the parts of a BAT reference document laying down the conclusions on best available techniques and emerging techniques, their description, information to assess their applicability, the emission levels associated with those techniques, the environmental performance levels associated with those techniques, the content of an environmental management system including benchmarks, associated monitoring, associated consumption levels and, where appropriate, relevant site remediation measures;
‘operating rules’ means the rules included in permits or general binding rules for the operation of activities referred to in Annex Ia, setting out the emission limit values, the environmental performance limit values, associated monitoring requirements, and, where relevant, land spreading practices, pollution prevention and mitigation practices, nutritional management, feed preparation, housing, manure management, including collection, storage, processing and land spreading of manure, and storage of dead animals, and which are consistent with the use of best available techniques;
‘emission levels associated with the best available techniques’ means the range of emission levels obtained under normal operating conditions using a best available technique or a combination of best available techniques, as described in BAT conclusions, expressed as an average over a given period of time, under specified reference conditions;
‘environmental performance levels associated with the best available techniques’ means the range of environmental performance levels, obtained under normal operating conditions using a BAT or a combination of BATs; as described in BAT conclusions;
‘environmental performance’ means the performance with regard to consumption levels, resource efficiency concerning materials, water and energy resources, the reuse of materials and water, and to waste generation;
‘benchmarks’ means the indicative range of environmental performance levels associated with best available techniques, which is to be used as a reference in the EMS;
‘emerging technique’ means a novel technique for an industrial activity that, if commercially developed, could provide either a higher general level of protection of human health and the environment or at least the same level of protection of human health and the environment and higher cost savings than existing best available techniques;
‘operator’ means any natural or legal person who operates or controls in whole or in part the installation or combustion plant, waste incineration plant or waste co-incineration plant or, where this is provided for in national law, to whom decisive economic power over the technical functioning of the installation or plant has been delegated;
‘the public’ means one or more natural or legal persons and, in accordance with national law or practice, their associations, organisations or groups;
‘the public concerned’ means the public affected or likely to be affected by, or having an interest in, the taking of a decision on the granting or the updating of a permit or of permit conditions; for the purposes of this definition, non-governmental organisations promoting the protection of human health or the environment and meeting any requirements under national law shall be deemed to have an interest;
‘hazardous substances’ means substances or mixtures as defined in Article 3 of Regulation (EC) No 1272/2008 of the European Parliament and of the Council of 16 December 2008 on classification, labelling and packaging of substances and mixtures ( 4 );
‘baseline report’ means information on the state of soil and groundwater contamination by relevant hazardous substances;
‘groundwater’ means groundwater as defined in point 2 of Article 2 of Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy ( 5 );
‘soil’ means the top layer of the Earth’s crust situated between the bedrock and the surface. The soil is composed of mineral particles, organic matter, water, air and living organisms;
‘environmental inspection’ means all actions, including site visits, monitoring of emissions and checks of internal reports and follow-up documents, verification of self-monitoring, checking of the techniques used and adequacy of the environment management of the installation, undertaken by or on behalf of the competent authority to check and promote compliance of installations with their permit conditions and, where necessary, to monitor their environmental impact;
‘poultry’ means poultry as defined in Article 4, point 9, of Regulation (EU) 2016/429 of the European Parliament and of the Council ( 6 );
‘pigs’ means pigs as defined in Article 2 of Council Directive 2008/120/EC ( 7 );
‘livestock unit’ means a standard measurement unit that allows for the aggregation of the various categories of livestock in order for them to be compared, and is calculated by using the coefficients for individual livestock categories listed in Annex Ia;
‘fuel’ means any solid, liquid or gaseous combustible material;
‘combustion plant’ means any technical apparatus in which fuels are oxidised in order to use the heat thus generated;
‘stack’ means a structure containing one or more flues providing a passage for waste gases in order to discharge them into the air;
‘operating hours’ means the time, expressed in hours, during which a combustion plant, in whole or in part, is operating and discharging emissions into the air, excluding start-up and shut-down periods;
‘rate of desulphurisation’ means the ratio over a given period of time of the quantity of sulphur which is not emitted into air by a combustion plant to the quantity of sulphur contained in the solid fuel which is introduced into the combustion plant facilities and which is used in the plant over the same period of time;
‘indigenous solid fuel’ means a naturally occurring solid fuel fired in a combustion plant specifically designed for that fuel and extracted locally;
‘determinative fuel’ means the fuel which, amongst all fuels used in a multi-fuel firing combustion plant using the distillation and conversion residues from the refining of crude-oil for own consumption, alone or with other fuels, has the highest emission limit value as set out in Part 1 of Annex V, or, in the case of several fuels having the same emission limit value, the fuel having the highest thermal input amongst those fuels;
‘biomass’ means any of the following:
products consisting of any vegetable matter from agriculture or forestry which can be used as a fuel for the purpose of recovering its energy content;
the following waste:
vegetable waste from agriculture and forestry;
vegetable waste from the food processing industry, if the heat generated is recovered;
fibrous vegetable waste from virgin pulp production and from production of paper from pulp, if it is co-incinerated at the place of production and the heat generated is recovered;
cork waste;
wood waste with the exception of wood waste which may contain halogenated organic compounds or heavy metals as a result of treatment with wood preservatives or coating and which includes, in particular, such wood waste originating from construction and demolition waste;
‘multi-fuel firing combustion plant’ means any combustion plant which may be fired simultaneously or alternately by two or more types of fuel;
‘gas turbine’ means any rotating machine which converts thermal energy into mechanical work, consisting mainly of a compressor, a thermal device in which fuel is oxidised in order to heat the working fluid, and a turbine;
‘gas engine’ means an internal combustion engine which operates according to the Otto cycle and uses spark ignition or, in case of dual fuel engines, compression ignition to burn fuel;
‘diesel engine’ means an internal combustion engine which operates according to the diesel cycle and uses compression ignition to burn fuel;
‘small isolated system’ means a small isolated system as defined in point 26 of Article 2 of Directive 2003/54/EC of the European Parliament and of the Council of 26 June 2003 concerning common rules for the internal market in electricity ( 8 );
‘waste’ means waste as defined in point 1 of Article 3 of Directive 2008/98/EC of the European Parliament and of the Council of 19 November 2008 on waste ( 9 );
‘hazardous waste’ means hazardous waste as defined in point 2 of Article 3 of Directive 2008/98/EC;
‘mixed municipal waste’ means waste from households as well as commercial, industrial and institutional waste which, because of its nature and composition, is similar to waste from households, but excluding fractions indicated under heading 20 01 of the Annex to Decision 2000/532/EC ( 10 ) that are collected separately at source and excluding the other waste indicated under heading 20 02 of that Annex;
‘waste incineration plant’ means any stationary or mobile technical unit and equipment dedicated to the thermal treatment of waste, with or without recovery of the combustion heat generated, through the incineration by oxidation of waste as well as other thermal treatment processes, such as pyrolysis, gasification or plasma process, if the substances resulting from the treatment are subsequently incinerated;
‘waste co-incineration plant’ means any stationary or mobile technical unit whose main purpose is the generation of energy or production of material products and which uses waste as a regular or additional fuel or in which waste is thermally treated for the purpose of disposal through the incineration by oxidation of waste as well as other thermal treatment processes, such as pyrolysis, gasification or plasma process, if the substances resulting from the treatment are subsequently incinerated;
‘nominal capacity’ means the sum of the incineration capacities of the furnaces of which a waste incineration plant or a waste co-incineration plant is composed, as specified by the constructor and confirmed by the operator, with due account being taken of the calorific value of the waste, expressed as the quantity of waste incinerated per hour;
‘dioxins and furans’ means all polychlorinated dibenzo-p-dioxins and dibenzofurans listed in Part 2 of Annex VI;
‘organic compound’ means any compound containing at least the element carbon and one or more of hydrogen, halogens, oxygen, sulphur, phosphorus, silicon or nitrogen, with the exception of carbon oxides and inorganic carbonates and bicarbonates;
‘volatile organic compound’ means any organic compound as well as the fraction of creosote, having at 293,15 K a vapour pressure of 0,01 kPa or more, or having a corresponding volatility under the particular conditions of use;
‘organic solvent’ means any volatile organic compound which is used for any of the following:
alone or in combination with other agents, and without undergoing a chemical change, to dissolve raw materials, products or waste materials;
as a cleaning agent to dissolve contaminants;
as a dissolver;
as a dispersion medium;
as a viscosity adjuster;
as a surface tension adjuster;
as a plasticiser;
as a preservative;
‘coating’ means coating as defined in point 8 of Article 2 of Directive 2004/42/EC of the European Parliament and of the Council of 21 April 2004 on the limitation of emissions of volatile organic compounds due to the use of organic solvents in certain paints and varnishes and vehicle refinishing products ( 11 );
‘emission levels associated with emerging techniques’ means the range of emission levels obtained under normal operating conditions using an emerging technique or a combination of emerging techniques, as described in BAT conclusions, expressed as an average over a given period of time, under specified reference conditions;
‘environmental performance levels associated with emerging techniques’ means the range of environmental performance levels, obtained under normal operating conditions, using an emerging technique or a combination of emerging techniques as described in BAT conclusions;
‘compliance assurance’ means mechanisms for securing compliance using three categories of intervention: compliance promotion; compliance monitoring; follow-up and enforcement.
Article 4
Obligation to hold a permit
Member States shall take the necessary measures to ensure that no installation or combustion plant, waste incineration plant or waste co-incineration plant is operated without a permit.
By way of derogation from the first subparagraph, Member States may set a procedure for the registration of installations covered only by Chapter V or Chapter VIa.
The procedure for registration shall be specified in a binding act and include at least a notification to the competent authority by the operator of the intention to operate an installation.
Member States may opt to provide that a permit cover two or more installations or parts of installations operated by the same operator on the same site.
Where a permit covers two or more installations, it shall contain conditions to ensure that each installation complies with the requirements of this Directive.
Article 5
Granting of a permit
The Commission shall organise an exchange of information with the Member States on electronic permitting and publish guidance on best practices.
Article 6
General binding rules
Without prejudice to the obligation to hold a permit, Member States may include requirements for certain categories of installations, combustion plants, waste incineration plants or waste co-incineration plants in general binding rules.
Where general binding rules are adopted, the permit may simply include a reference to such rules.
Article 7
Incidents and accidents
Without prejudice to Directive 2004/35/EC of the European Parliament and of the Council ( 12 ), in the event of any incident or accident significantly affecting human health or the environment, Member States shall take the necessary measures to ensure that:
the operator informs the competent authority immediately;
the operator immediately takes the measures to limit the consequences for human health or the environment and to prevent further possible incidents or accidents; and
the competent authority requires the operator to take any appropriate complementary measures that the competent authority considers necessary to limit the consequences for human health or the environment and to prevent further possible incidents or accidents.
In the event of pollution affecting drinking water resources, including transboundary resources, or affecting waste water infrastructure in the case of indirect discharge, the competent authority shall inform the drinking water and waste water operators affected of the measures taken to prevent damage being caused, or remedy the damage caused, by that pollution to human health and the environment.
In the event of any incident or accident significantly affecting human health or the environment in another Member State, the Member State in whose territory the accident or incident has occurred shall ensure that the competent authority of the other Member State is immediately informed. Transboundary and multidisciplinary cooperation between the affected Member States shall be aimed at limiting the consequences for the environment and human health and to prevent further possible incidents or accidents.
Article 8
Non-compliance
They shall also adopt compliance assurance measures to promote, monitor and enforce compliance with obligations placed on natural or legal persons under this Directive.
In the event of a breach of the permit conditions, Member States shall ensure that:
the operator immediately informs the competent authority;
the operator immediately takes the measures necessary to ensure that compliance is restored within the shortest possible time; and
the competent authority requires the operator to take any appropriate complementary measures that the competent authority considers necessary to restore compliance.
Where such breach threatens human health or the environment in another Member State, the Member State in whose territory the breach of the permit conditions has occurred shall ensure that the other Member State is informed.
Article 9
Emission of greenhouse gases
CHAPTER II
PROVISIONS FOR ACTIVITIES LISTED IN ANNEX I
Article 10
Scope
This Chapter shall apply to the activities set out in Annex I and, where applicable, reaching the capacity thresholds set out in that Annex.
Article 11
General principles governing the basic obligations of the operator
Member States shall take the necessary measures to provide that installations are operated in accordance with the following principles:
all the appropriate preventive measures are taken against pollution;
the best available techniques are applied;
no significant pollution is caused;
the generation of waste is prevented in accordance with Directive 2008/98/EC;
where waste is generated, it is, in order of priority and in accordance with Directive 2008/98/EC, prepared for re-use, recycled, recovered or, where that is technically and economically impossible, it is disposed of while avoiding or reducing any impact on the environment;
energy is used efficiently and the use and, where possible, the production of renewable energy is promoted;
material resources and water are used efficiently, including through re-use;
an environmental management system is implemented as provided for in Article 14a;
the necessary measures are taken to prevent accidents and limit their consequences;
the necessary measures are taken upon definitive cessation of activities to avoid any risk of pollution and return the site of operation to the satisfactory state defined in accordance with Article 22.
Article 12
Applications for permits
Member States shall take the necessary measures to ensure that an application for a permit includes a description of the following:
the installation and its activities;
the raw and auxiliary materials, other substances, the energy and water used in or generated by the installation;
the sources of emissions from the installation, including odours;
the conditions of the site of the installation;
where applicable, a baseline report in accordance with Article 22(2);
the nature and quantities of foreseeable emissions, including odours, from the installation into each medium, as well as an identification of significant effects of the emissions on the environment;
the proposed technology and other techniques for preventing or, where this is not possible, reducing emissions from the installation;
measures for the prevention, preparation for re-use, recycling and recovery of waste generated by the installation;
further measures planned to comply with the general principles of the basic obligations of the operator as provided for in Article 11;
measures planned to monitor emissions into the environment;
the main alternatives to the proposed technology, techniques and measures studied by the applicant in outline.
An application for a permit shall also include a non-technical summary of the details referred to in the first subparagraph.
Article 13
BAT reference documents and exchange of information
The exchange of information shall, in particular, address the following:
the performance of installations and techniques in terms of emissions, expressed as short- and long-term averages, where appropriate, and the associated reference conditions, consumption and nature of raw materials, water consumption, use of energy and generation of waste;
the techniques used, associated monitoring, cross-media effects, economic and technical viability and developments therein;
best available techniques and emerging techniques identified after considering the issues mentioned in points (a) and (b).
Without prejudice to Union competition law, information considered to be confidential business information or commercially sensitive information shall only be shared with the Commission and, after having signed a confidentiality and non-disclosure agreement, with civil servants and other public employees representing Member States or Union agencies. Information shall be anonymised, in such a manner that it does not refer to a particular operator or installation, when shared with the other stakeholders involved in the exchange of information referred to in paragraph 1. Non-anonymised information may only be shared in cases where anonymising the information would not allow an effective exchange of information on BAT in the context of drawing up, reviewing and, where necessary, updating BAT reference documents, with representatives of non-governmental organisations promoting the protection of human health or the environment and representatives of associations representing the relevant industrial sectors, as appropriate, and where such representatives of organisations and associations have signed a confidentiality and non-disclosure agreement. The exchange of information considered to be confidential business information or commercially sensitive information shall remain strictly limited to what is technically required to draw up, review and, where necessary, update BAT reference documents, and such confidential business information or commercially sensitive information shall not be used for other purposes.
►M1 The Commission shall establish and regularly convene a forum composed of representatives of Member States, the industries concerned and non-governmental organisations promoting the protection of human health or the environment. ◄
The Commission shall obtain the opinion of the forum on the practical arrangements for the exchange of information and, in particular, on the following:
the rules of procedure of the forum;
the work programme for the exchange of information;
guidance on the collection of data;
guidance on the drawing up of BAT reference documents, and on their quality assurance including the suitability of their content and format.
The guidance referred to in points (c) and (d) of the second subparagraph shall take account of the opinion of the forum and shall be adopted in accordance with the regulatory procedure referred to in Article 75(2).
The opinion of the forum referred to in the first subparagraph shall be submitted within six months of the final meeting of the technical working group responsible for that BAT reference document.
Article 14
Permit conditions
►M1 Member States shall ensure that the permit includes all measures necessary to comply with the requirements of Articles 11 and 18. To that effect, Member States shall ensure that permits are granted further to consultation of all relevant authorities with a responsibility regarding compliance with Union environmental legislation, including with environmental quality standards. ◄
Those measures shall include at least the following:
emission limit values for polluting substances listed in Annex II to Regulation (EC) No 166/2006, and for other polluting substances, which are likely to be emitted from the installation concerned in significant quantities, having regard to their nature, their hazardousness and their potential to transfer pollution from one medium to another, taking into account the variation of water flow dynamics in receiving water bodies;
environmental performance limit values in accordance with Article 15(4);
appropriate requirements ensuring the assessment of the need to prevent or reduce the emissions of substances fulfilling the criteria of Article 57 or substances addressed in restrictions in Annex XVII to regulation (EC) No 1907/2006;
appropriate requirements ensuring protection of the soil, groundwater, surface water and catchment areas for abstraction points of water intended for human consumption as referred to in Article 7 of Directive (EU) 2020/2184, and measures concerning the monitoring and management of waste generated by the installation;
appropriate requirements laying down the characteristics of an environmental management system in accordance with Article 14a;
suitable monitoring requirements for the consumption and reuse of resources such as energy, water and raw materials;
suitable emission monitoring requirements specifying:
measurement methodology, frequency and evaluation procedure; and
where Article 15(3)(b) is applied, that results of emission monitoring are available for the same periods of time and reference conditions as for the emission levels associated with the best available techniques;
an obligation to supply the competent authority regularly, and at least annually, with:
information on the basis of results of emission monitoring referred to in point (c) and other required data that enables the competent authority to verify compliance with the permit conditions; and
where Article 15(3)(b) is applied, a summary of the results of emission monitoring which allows a comparison with the emission levels associated with the best available techniques;
information on progress towards fulfilment of the environmental policy objectives referred to in Article 14a;
appropriate requirements for the regular maintenance and surveillance of measures taken to prevent emissions to soil, surface and groundwater pursuant to point (b), and appropriate requirements concerning the periodic monitoring of soil, surface and groundwater in relation to relevant hazardous substances likely to be found on site and having regard to the possibility of soil, surface and groundwater contamination at the site of the installation;
measures relating to conditions other than normal operating conditions such as start-up and shut-down operations, leaks, malfunctions, momentary stoppages and definitive cessation of operations;
provisions on the minimisation of long-distance or transboundary pollution;
conditions for assessing compliance with the emission limit values and environmental performance limit values or a reference to the applicable requirements specified elsewhere.
Where the competent authority sets permit conditions on the basis of a best available technique not described in any of the relevant BAT conclusions, it shall ensure that:
that technique is determined by giving special consideration to the criteria listed in Annex III; and
the requirements of Article 15 are complied with.
Where the BAT conclusions referred to in the first subparagraph do not contain emission levels associated with the best available techniques, the competent authority shall ensure that the technique referred to in the first subparagraph ensures a level of environmental protection equivalent to the best available techniques described in the BAT conclusions.
Article 14a
Environmental management system
The EMS shall include at least the following:
environmental policy objectives for the continuous improvement of the environmental performance and safety of the installation, which shall include measures to:
prevent the generation of waste;
optimise resource and energy use and water reuse;
prevent or reduce the use or emissions of hazardous substances;
objectives and performance indicators in relation to significant environmental aspects, which shall take into account benchmarks set out in the relevant BAT conclusions;
for installations covered by the obligation to conduct an energy audit or implement an energy management system pursuant to Article 8 of Directive 2012/27/EU, inclusion of the results of that audit or implementation of the energy management system pursuant to Article 8 of and Annex VI to that Directive and of the measures to implement their recommendations;
a chemicals inventory of the hazardous substances present in or emitted from the installation as such, as constituents of other substances or as part of mixtures, with special regard given to the substances fulfilling the criteria referred to in Article 57 of Regulation (EC) No 1907/2006 and substances addressed in restrictions referred to in Annex XVII to Regulation (EC) No 1907/2006, and a risk assessment of the impact of such substances on human health and the environment, as well as an analysis of the possibilities for substituting them with safer alternatives or reducing their use or emissions;
measures taken to achieve the environmental objectives and avoid risks for human health or the environment, including corrective and preventive measures where needed;
a transformation plan as referred to in Article 27d.
Where elements required to be included in the EMS, including objectives, performance indicators or measures, have already been developed in accordance with other relevant Union legislation and comply with this Article, a reference in the EMS to the relevant documents shall be sufficient.
The Commission shall, by 31 December 2025, adopt an implementing act on which information is relevant for publication. That implementing act shall be adopted in accordance with the examination procedure referred to in Article 75(2).
Information may be redacted or, if that is not possible, excluded when made available on the internet, if the disclosure of the information would adversely affect any of the interests listed in Article 4(2), points (a) to (h) of Directive 2003/4/EC.
The operator shall prepare and implement the EMS in accordance with the relevant BAT conclusions for the sector by 1 July 2027, except for installations referred to in Article 3(4) of Directive (EU) 2024/1785 of the European Parliament and of the Council ( 13 ).
The EMS shall be reviewed periodically to ensure that it continues to be suitable, adequate and effective.
The EMS shall be audited for the first time by 1 July 2027 except for installations referred to in Article 3(4) of Directive (EU) 2024/1785. The EMS shall be audited at least every 3 years, by a conformity assessment body accredited in accordance with Regulation (EC) No 765/2008 or an accredited or licensed environmental verifier as defined in Article 2, point 20 of Regulation (EC) No 1221/2009, who verifies the conformity of the EMS, and of its implementation, with this Article.
Article 15
Emission limit values, environmental performance limit values, equivalent parameters and technical measures
With regard to indirect releases of polluting substances into water, the effect of a waste water treatment plant outside the installation may be taken into account when determining the emission limit values of the installation concerned, provided that this does not lead to higher levels of pollution in the environment, an equivalent level of protection of the environment as a whole is guaranteed, and the operator ensures, in consultation with the operator of the waste water treatment plant, that the indirect releases do not jeopardise compliance with the provisions of the permit of the waste water treatment plant under this Directive or the specific authorisation under Directive 91/271/EEC and that all of the following requirements are fulfilled:
the released polluting substances do not impede the operation of the waste water treatment plant or the capacity to recover resources from the waste water treatment stream;
the released polluting substances do not harm the health of the staff working in collecting systems and waste water treatment plants;
the waste water treatment plant is designed and equipped to abate the released polluting substances;
the overall load of the concerned polluting substances eventually released into the water is not increased compared to the situation where the emissions from the installation concerned remained compliant with emission limit values set for direct releases in accordance with paragraph 3 of this Article, without prejudice to stricter measures required pursuant to Article 18.
The competent authority shall set out in an annex to the permit conditions the reasons for the application of the second subparagraph, including the result of the assessment by the operator of the fulfilment of the required conditions.
The operator shall provide an updated assessment in cases where the permit conditions should be changed to ensure that the requirements set out in the second subparagraph, points (a) to (d) are fulfilled.
The competent authority shall set the strictest achievable emission limit values by applying BAT in the installation, considering the entire range of the emission levels associated with the best available techniques (“BAT-AELs”) to ensure that, under normal operating conditions, emissions do not exceed the BAT-AELs as laid down in the decisions on BAT conclusions referred to in Article 13(5). The emission limit values shall be based on an assessment by the operator of the entire BAT-AEL range, analysing the feasibility of meeting the strictest end of the BAT-AEL range and demonstrating the best overall performance that the installation can achieve by applying BAT as described in BAT conclusions, having regard to possible cross-media effects. The emission limit values shall be set through either of the following:
setting emission limit values expressed for the same or shorter periods of time and under the same reference conditions as the BAT-AELs; or
setting emission limit values different from those referred to in point (a) in terms of values, periods of time and reference conditions.
Where the emission limit values are set in accordance with point (b), the competent authority shall, at least annually, assess the results of emission monitoring in order to ensure that emissions under normal operating conditions have not exceeded the BAT-AELs.
General binding rules referred to in Article 6 may be applied while setting relevant emission limit values in accordance with this Article.
If general binding rules are adopted, the strictest achievable emission limit values by applying BAT shall be set for categories of installations having similar characteristics that are relevant in determining the lowest emission levels achievable, considering the entire range of the BAT-AELs. The general binding rules shall be established by the Member State, based on the information in the BAT conclusions, analysing the feasibility of meeting the strictest end of the BAT-AEL range and demonstrating the best performance that those categories of installations can achieve by applying BAT as described in BAT conclusions.
In addition, the competent authority shall:
set, for normal operating conditions, environmental performance limit values concerning water, having regard to possible cross-media effects, that are not to be exceeded during one or more periods, and which are not less strict than the binding ranges referred to in the first subparagraph;
set, for normal operating conditions, indicative environmental performance levels concerning waste and resources other than water, which are not less strict than the binding ranges referred to in the first subparagraph.
By way of derogation from paragraph 3, and without prejudice to Article 18, the competent authority may, in specific cases, set emission limit values higher than the BAT-AELs. Such a derogation may apply only where an assessment shows that the achievement of BAT-AELs as described in BAT conclusions would lead to disproportionately higher costs compared to the environmental benefits due to:
the geographical location or the local environmental conditions of the installation concerned; or
the technical characteristics of the installation concerned.
The competent authority shall document in an annex to the permit conditions the reasons for derogating from paragraph 3, and the result of the assessment referred to in the first subparagraph of this paragraph and the justification for the conditions imposed.
The emission limit values set in accordance with the first subparagraph shall, however, not exceed the emission limit values set out in the Annexes to this Directive, where applicable.
Derogations granted in accordance with this paragraph shall respect the principles set out in Annex II. The competent authority shall ensure that the operator provides an assessment of the impact of the derogation on the concentration of the pollutants concerned in the receiving environment and in any case ensure that no significant pollution is caused and that a high level of protection of the environment as a whole is achieved. Derogations shall not be granted where they could put at risk compliance with environmental quality standards referred to in Article 18.
The competent authority shall re-assess whether derogations granted in accordance with this paragraph are justified, every four years or as part of each reconsideration of the permit conditions pursuant to Article 21, where such reconsideration occurs earlier than four years after the derogation was granted.
The Commission shall adopt an implementing act to establish a standardised methodology for assessing the disproportionality between the costs of implementation of the BAT conclusions and the potential environmental benefits referred to in the first subparagraph. That implementing act shall be adopted in accordance with the examination procedure referred to in Article 75(2).
By way of derogation from paragraph 4, the competent authority may, in specific cases, set less strict binding ranges for environmental performance or environmental performance limit values. Such a derogation may apply only where an assessment shows that the achievement of performance levels associated with the best available techniques as described in BAT conclusions will lead to a significant negative environmental impact, including cross media effects, or a significant economic impact due to:
the geographical location or the local environmental conditions of the installation concerned; or
the technical characteristics of the installation concerned.
The competent authority shall document in an annex to the permit conditions the reasons for derogating from paragraph 4 and the result of the assessment referred to in the first subparagraph of this paragraph and the justification for the conditions imposed.
The competent authority shall ensure that operating under less strict binding ranges for environmental performance or environmental performance limit values does not cause any significant environmental impact, including depletion of water resources, and achieves a high level of protection of the environment as a whole.
The Commission shall establish, by means of implementing acts, a standardised methodology for undertaking the assessment referred to in the first subparagraph. Those implementing acts shall be adopted in accordance with the examination procedure referred to in Article 75(2).
By way of derogation from paragraphs 3 and 4, and provided that no significant pollution is caused and all measures resulting in less pollution have been exhausted, the competent authority may set less strict emission limit values or environmental performance limit values in the event of a crisis due to extraordinary circumstances beyond the control of the operator and Member States, leading to a severe disruption or shortage of:
energy supplies, provided that there is an overriding public interest in security of energy supply;
resources, materials or equipment essential for the operator to perform activities of public interest, in compliance with the applicable emission limit values or environmental performance limit values; or
essential resources, materials or equipment where the production output compensates for such shortage or disruption, for reasons of public health or public safety or for other imperative reasons of overriding public interest.
The derogation shall not be granted for more than three months. If the reasons justifying the granting of a derogation persist, the derogation may be prolonged for a maximum period of three months.
As soon as the supply conditions are restored or where there is an alternative to the energy supplies, resources, materials or equipment, the Member State shall ensure that the decision to set less strict emission limit values and environmental performance limit values ceases to have effect, and the installation shall comply with permit conditions set in accordance with paragraphs 3 and 4.
The Member States shall take measures to ensure that emissions resulting from the derogation referred to in the first subparagraph are monitored.
The competent authority shall make information on the derogation and the conditions imposed publicly available in accordance with Article 24(2).
The Commission may, where necessary, assess and further clarify, through guidance, the criteria to be taken into account for the application of this paragraph.
Member States shall notify the Commission of any derogation granted under this paragraph, including the reasons justifying the granting of the derogation and the conditions imposed.
The Commission shall assess whether the derogation granted is justified having due regard to the criteria set in this paragraph. If the Commission raises objections within 2 months of the notification by the Member State, the Member States shall without delay revise the derogation accordingly.
Article 15a
Compliance assessment
The method referred to in the first subparagraph shall address, as a minimum, the determination of validated average emission values and shall set out how measurement uncertainty and the frequency of exceedance of emission limit values are to be taken into account in the compliance assessment.
Article 16
Monitoring requirements
Without prejudice to the first subparagraph, periodic monitoring shall be carried out as set out in the BAT conclusions, where applicable, and at least once every 4 years for groundwater and 9 years for soil, unless such monitoring is based on a systematic appraisal of the risk of contamination.
Article 17
General binding rules for activities listed in Annex I
Article 18
Environmental quality standards
Where an environmental quality standard requires stricter conditions than those achievable by the use of the best available techniques, additional measures shall be included in the permit, with a view to reducing the specific contribution of the installation to the pollution occurring in the relevant area, without prejudice to other measures which may be taken to comply with environmental quality standards.
Where stricter conditions have been included in the permit in accordance with the first paragraph, the competent authority shall assess the impact of the stricter conditions on the concentration of the pollutants concerned in the receiving environment.
Where the load of pollutants emitted by the installation has a quantifiable or measurable effect on the environment, Member States shall ensure that the concentration of the pollutants concerned in the receiving environment is monitored. The results of such monitoring shall be transmitted to the competent authority.
Where monitoring and measurement methods for the pollutants concerned are set out in other relevant Union legislation, such methods, including effect-based methods as appropriate, shall be used for the purpose of the monitoring referred to in the third paragraph.
Article 19
Developments in best available techniques
Member States shall ensure that the competent authority follows or is informed of developments in best available techniques and of the publication of any new or updated BAT conclusions and shall make that information available to the public concerned.
Article 20
Changes by operators to installations
Member States shall take the necessary measures to ensure that no substantial change planned by the operator is made without a permit granted in accordance with this Directive.
The application for a permit and the decision by the competent authority shall cover those parts of the installation and those details listed in Article 12 which may be affected by the substantial change.
Article 21
Reconsideration and updating of permit conditions by the competent authority
At the request of the competent authority, the operator shall submit all the information necessary for the purpose of reconsidering the permit conditions, including, in particular, results of emission monitoring and other data, that enables a comparison of the operation of the installation with the best available techniques described in the applicable BAT conclusions and with the emission levels associated with the best available techniques.
When reconsidering permit conditions, the competent authority shall use any information resulting from monitoring or inspections.
Within 4 years of publication of decisions on BAT conclusions in accordance with Article 13(5) relating to the main activity of an installation, the competent authority shall ensure that:
all the permit conditions for the installation concerned are reconsidered and, if necessary, updated to ensure compliance with this Directive, in particular, with Article 15(3), (4) and (5), where applicable;
the installation complies with those permit conditions.
The reconsideration shall take into account all the new or updated BAT conclusions applicable to the installation and adopted in accordance with Article 13(5) since the permit was granted or last reconsidered.
The permit conditions shall be reconsidered and, where necessary, updated at least in the following cases:
the pollution caused by the installation is of such significance that the existing emission limit values of the permit need to be revised or new such values need to be included in the permit;
the operational safety requires other techniques to be used;
where it is necessary to comply with an environmental quality standard referred to in Article 18, including in the case of a new or revised quality standard or where the status of the receiving environment requires a revision of the permit in order to achieve compliance with plans and programmes set under Union legislation;
in the case of a request from the operator to extend the duration of the operation of an installation undertaking the activity referred to in Annex I, point 5.4.
Article 22
Site closure
Where the activity involves the use, production or release of relevant hazardous substances and having regard to the possibility of soil and groundwater contamination at the site of the installation, the operator shall prepare and submit to the competent authority a baseline report before starting operation of an installation or before a permit for an installation is updated for the first time after 7 January 2013.
The baseline report shall contain the information necessary to determine the state of soil and groundwater contamination so as to make a quantified comparison with the state upon definitive cessation of activities provided for under paragraph 3.
The baseline report shall contain at least the following information:
information on the present use and, where available, on past uses of the site;
where available, existing information on soil and groundwater measurements that reflect the state at the time the report is drawn up or, alternatively, new soil and groundwater measurements having regard to the possibility of soil and groundwater contamination by those hazardous substances to be used, produced or released by the installation concerned.
Where information produced pursuant to other national or Union law fulfils the requirements of this paragraph that information may be included in, or attached to, the submitted baseline report.
The Commission shall establish guidance on the content of the baseline report.
Upon definitive cessation of the activities, the operator shall assess the state of soil and groundwater contamination by relevant hazardous substances used, produced or released by the installation. Where the installation has caused significant pollution of soil or groundwater by relevant hazardous substances compared to the state established in the baseline report referred to in paragraph 2, the operator shall take the necessary measures to address that pollution so as to return the site to that state. For that purpose, the technical feasibility of such measures may be taken into account.
Without prejudice to the first subparagraph, upon definitive cessation of the activities, and where the contamination of soil and groundwater at the site poses a significant risk to human health or the environment as a result of the permitted activities carried out by the operator before the permit for the installation is updated for the first time after 7 January 2013 and taking into account the conditions of the site of the installation established in accordance with Article 12(1)(d), the operator shall take the necessary actions aimed at the removal, control, containment or reduction of relevant hazardous substances, so that the site, taking into account its current or approved future use, ceases to pose such a risk.
Article 23
Environmental inspections
Member States shall set up a system of environmental inspections of installations addressing the examination of the full range of relevant environmental effects from the installations concerned.
Member States shall ensure that operators afford the competent authorities all necessary assistance to enable those authorities to carry out any site visits, to take samples and to gather any information necessary for the performance of their duties for the purposes of this Directive.
Each environmental inspection plan shall include the following:
a general assessment of relevant significant environmental issues;
the geographical area covered by the inspection plan;
a register of the installations covered by the plan;
procedures for drawing up programmes for routine environmental inspections pursuant to paragraph 4;
procedures for non-routine environmental inspections pursuant to paragraph 5;
where necessary, provisions on the cooperation between different inspection authorities.
Based on the inspection plans, the competent authority shall regularly draw up programmes for routine environmental inspections, including the frequency of site visits for different types of installations.
The period between two site visits shall be based on a systematic appraisal of the environmental risks of the installations concerned and shall not exceed 1 year for installations posing the highest risks and 3 years for installations posing the lowest risks.
If an inspection has identified an important case of non-compliance with the permit conditions, an additional site visit shall be carried out within 6 months of that inspection.
The systematic appraisal of the environmental risks shall be based on at least the following criteria:
the potential and actual impacts of the installations concerned on human health and the environment taking into account the levels and types of emissions, the sensitivity of the local environment and the risk of accidents;
the record of compliance with permit conditions;
the participation of the operator in the Union eco-management and audit scheme (EMAS), pursuant to Regulation (EC) No 1221/2009 ( 15 ).
The Commission shall adopt and, where appropriate, regularly update guidance on the criteria for the appraisal of environmental risks.
Following each site visit, the competent authority shall prepare a report describing the relevant findings regarding compliance of the installation with the permit conditions and conclusions on whether any further action is necessary.
The report shall be notified to the operator concerned within 2 months of the site visit taking place. The report shall be made publicly available by the competent authority in accordance with Directive 2003/4/EC of the European Parliament and of the Council of 28 January 2003 on public access to environmental information ( 16 ) within 4 months of the site visit taking place.
Without prejudice to Article 8(2), the competent authority shall ensure that the operator takes all the necessary actions identified in the report within a reasonable period.
Article 24
Access to information and public participation in the permit procedure
Member States shall ensure that the public concerned are given early and effective opportunities to participate in the following procedures:
the granting of a permit for new installations;
the granting of a permit for any substantial change;
the granting or updating of a permit for an installation where the application of Article 15(4) is proposed;
the updating of a permit or permit conditions for an installation in accordance with Article 21(5);
the updating of a permit in accordance with Article 21(3) or Article 21(4).
The procedure set out in Annex IV shall apply to such participation.
When a decision on granting or the reconsideration or updating of a permit has been taken, the competent authority shall make available to the public, including systematically via the internet, on a webpage which is easy to find, free of charge and without restricting access to registered users, in relation to points (a), (b) and (f), the following information:
the content of the decision, including a copy of the permit and any subsequent updates, including consolidated permit conditions where relevant;
the reasons on which the decision is based;
the results of the consultations held before the decision was taken, including consultations held pursuant to Article 26, and an explanation of how those consultations were taken into account in that decision;
the title of the BAT reference documents relevant to the installation or activity concerned;
how the permit conditions referred to in Article 14, including the emission limit values, environmental performance levels and environmental performance limit values, have been determined in relation to the best available techniques and emission levels and environmental performance levels associated with the best available techniques;
where a derogation is granted in accordance with Article 15, the specific reasons for that derogation based on the criteria laid down in that paragraph and the conditions imposed.
The competent authority shall also make available to the public, including systematically via the internet, on a webpage which is easy to find, free of charge and without restricting access to registered users, the following:
relevant information on the measures taken by the operator upon definitive cessation of activities in accordance with Article 22;
the results of emission monitoring as required under the permit conditions and held by the competent authority;
the results of the monitoring referred to in Article 16(4) and in Article 18.
Article 25
Access to justice
Member States shall ensure that, in accordance with the relevant national legal system, members of the public concerned have access to a review procedure before a court of law or another independent and impartial body established by law to challenge the substantive or procedural legality of decisions, acts or omissions subject to Article 24 when one of the following conditions is met:
they have a sufficient interest;
they maintain the impairment of a right, where administrative procedural law of a Member State requires this as a precondition.
Standing in the review procedure shall not be conditional on the role that the member of the public concerned played during a participatory phase of the decision-making procedures under this Directive.
The review procedure shall be fair, equitable, timely and not prohibitively expensive, and shall provide for adequate and effective remedies, including injunctive relief as appropriate.
What constitutes a sufficient interest and impairment of a right shall be determined by Member States, consistently with the objective of giving the public concerned wide access to justice.
To this end, the interest of any non-governmental organisation promoting environmental protection and meeting any requirements under national law shall be deemed sufficient for the purpose of paragraph 1(a).
Such organisations shall also be deemed to have rights capable of being impaired for the purpose of paragraph 1(b).
Paragraphs 1, 2 and 3 shall not exclude the possibility of a preliminary review procedure before an administrative authority and shall not affect the requirement of exhaustion of administrative review procedures prior to recourse to judicial review procedures, where such a requirement exists under national law.
Any such procedure shall be fair, equitable, timely and not prohibitively expensive.
Article 26
Transboundary effects
CHAPTER IIA
ENABLING AND PROMOTING INNOVATION
Article 27
Emerging techniques
Member States shall, where appropriate, encourage the development and application of emerging techniques, in particular where such techniques have been identified in the BAT conclusions, the BAT reference documents or the findings of the innovation centre for industrial transformation and emissions referred to in Article 27a.
Article 27a
Innovation centre for industrial transformation and emissions
The centre shall be assisted by:
representatives of Member States;
relevant public institutions;
relevant research institutes;
research and technology organisations;
representatives of the industries and farmers concerned;
technology providers;
non-governmental organisations promoting the protection of human health or the environment;
the Commission.
The Commission shall adopt an implementing act setting out the detailed arrangements necessary for the establishment and functioning of the centre. That implementing act shall be adopted in accordance with the examination procedure referred to in Article 75(2).
Article 27b
Testing of emerging techniques
Without prejudice to Article 18, the competent authority may grant temporary derogations from the requirements set out in Article 15(2), (3) and (4) and from the principles set out in Article 11, points (a) and (b), for the testing of emerging techniques for a total period of time not exceeding 30 months, provided that after the period specified in the permit, either the testing of the technique is stopped or the activity achieves at least the BAT-AELs.
Article 27c
Emission levels and indicative environmental performance values associated with emerging techniques
By way of derogation from Article 21(3), the competent authority may set:
emission limit values that ensure that, within 6 years of publication of a decision on BAT conclusions in accordance with Article 13(5) relating to the main activity of an installation, emissions do not, under normal operating conditions, exceed emission levels associated with emerging techniques as laid down in the decisions on BAT conclusions;
indicative environmental performance values consistent with the decisions on BAT conclusions.
Article 27d
Transformation towards a clean, circular and climate-neutral industry
Member States shall take the necessary measures to ensure that, no later than a year after the deadline set out in the first subparagraph of this paragraph, the audit organisation referred to in Article 14a(4), sixth subparagraph, assesses the conformity of the transformation plans referred to in the first subparagraph of this paragraph with the requirements set out in the delegated act referred to in paragraph 5 of this Article.
Member States shall take the necessary measures to ensure that, no later than a year after completion of the review referred to in Article 21(3), the audit organisation referred to in Article 14a(4), sixth subparagraph, assesses the conformity of the transformation plans referred to in the first subparagraph with the requirements set out in the delegated act referred to in paragraph 5 of this Article.
Where elements of the transformation plans have already been developed in accordance with other Union legislation and are compliant with this Article, a reference may be made in the transformation plan to the relevant documents.
The Commission shall, by 31 December 2034, review and, where appropriate, revise the delegated act referred to in the first subparagraph.
Article 27e
Deep industrial transformation
Without prejudice to Article 18, in the event of deep industrial transformation of the installation set out in the relevant transformation plan covering the installation, the competent authority may extend the period for the installation to comply with the updated permit conditions referred to in Article 21(3) up to a total of eight years maximum, provided that:
the permit for the installation contains a description of the deep industrial transformation, the emission levels and the resource efficiency that will be achieved, and the implementation timeline and milestones;
the operator reports annually to the competent authority on the progress in the implementation of the deep industrial transformation; and
during the period granted for the transformation of the installation, the competent authority ensures that no significant pollution is caused and that a high level of protection of the environment as a whole is achieved.
Member States shall inform the Commission at least yearly of derogations granted as part of their reporting to the Commission under Article 72.
Without prejudice to Articles 18 and 22, in the event of deep industrial transformation consisting of the closure of an installation and its replacement by a new installation set out in the relevant transformation plan covering the installation and to be completed within 8 years of publication of decisions on BAT conclusions, in accordance with Article 13(5), relating to the main activity of the existing installation, the competent authority may waive the obligation of updating the permit in accordance with Article 21(3), provided that all the following conditions are met:
the permit for the existing installation contains a description of the closure plan and the associated timeline and milestones;
the operator reports annually to the competent authority on the progress in relation to the closure plan for the existing installation and to its replacement by a new installation;
during the period preceding the closure of the installation, the competent authority ensures that no significant pollution is caused and that a high level of protection of the environment as a whole is achieved.
Member States shall inform the Commission as part of their reporting under Article 72 at least yearly of derogations granted.
CHAPTER III
SPECIAL PROVISIONS FOR COMBUSTION PLANTS
Article 28
Scope
This Chapter shall apply to combustion plants, the total rated thermal input of which is equal to or greater than 50 MW, irrespective of the type of fuel used.
This Chapter shall not apply to the following combustion plants:
plants in which the products of combustion are used for the direct heating, drying, or any other treatment of objects or materials;
post-combustion plants designed to purify the waste gases by combustion which are not operated as independent combustion plants;
facilities for the regeneration of catalytic cracking catalysts;
facilities for the conversion of hydrogen sulphide into sulphur;
reactors used in the chemical industry;
coke battery furnaces;
cowpers;
any technical apparatus used in the propulsion of a vehicle, ship or aircraft;
gas turbines and gas engines used on offshore platforms;
plants which use any solid or liquid waste as a fuel other than waste referred to in point (b) of point 31 of Article 3.
Article 29
Aggregation rules
Article 30
Emission limit values
All permits for installations containing combustion plants which have been granted a permit before 7 January 2013, or the operators of which have submitted a complete application for a permit before that date, provided that such plants are put into operation no later than 7 January 2014, shall include conditions ensuring that emissions into air from these plants do not exceed the emission limit values set out in Part 1 of Annex V.
All permits for installations containing combustion plants which had been granted an exemption as referred to in Article 4(4) of Directive 2001/80/EC and which are in operation after 1 January 2016, shall include conditions ensuring that emissions into the air from these plants do not exceed the emission limit values set out in Part 2 of Annex V.
Member States shall immediately inform the Commission of any derogation granted under the first subparagraph, including the reasons justifying the derogation and the conditions imposed.
The competent authority may grant a derogation from the obligation to comply with the emission limit values provided for in paragraphs 2 and 3 in cases where a combustion plant using only gaseous fuel has to resort exceptionally to the use of other fuels because of a sudden interruption in the supply of gas and for this reason would need to be equipped with a waste gas purification facility. The period for which such a derogation is granted shall not exceed 10 days except where there is an overriding need to maintain energy supplies.
The operator shall immediately inform the competent authority of each specific case referred to in the first subparagraph.
Member States shall inform the Commission immediately of any derogation granted under the first subparagraph, including the reasons justifying the derogation and the conditions imposed.
The emission limit values set out in Parts 1 and 2 of Annex V shall not apply to the following combustion plants:
diesel engines;
recovery boilers within installations for the production of pulp.
For the following combustion plants, on the basis of the best available techniques, the Commission shall review the need to establish Union-wide emission limit values and to amend the emission limit values set out in Annex V:
the combustion plants referred to in paragraph 8;
combustion plants within refineries firing the distillation and conversion residues from the refining of crude-oil for own consumption, alone or with other fuels, taking into account the specificity of the energy systems of refineries;
combustion plants firing gases other than natural gas;
combustion plants in chemical installations using liquid production residues as non-commercial fuel for own consumption.
The Commission shall, by 31 December 2013, report the results of this review to the European Parliament and to the Council accompanied, if appropriate, by a legislative proposal.
Article 31
Desulphurisation rate
Article 32
Transitional National Plan
During the period from 1 January 2016 to 30 June 2020, Member States may draw up and implement a transitional national plan covering combustion plants which were granted the first permit before 27 November 2002 or the operators of which had submitted a complete application for a permit before that date, provided that the plant was put into operation no later than 27 November 2003. For each of the combustion plants covered by the plan, the plan shall cover emissions of one or more of the following pollutants: nitrogen oxides, sulphur dioxide and dust. For gas turbines, only nitrogen oxides emissions shall be covered by the plan.
The transitional national plan shall not include any of the following combustion plants:
those to which Article 33(1) applies;
those within refineries firing low calorific gases from the gasification of refinery residues or the distillation and conversion residues from the refining of crude oil for own consumption, alone or with other fuels;
those to which Article 35 applies;
those which are granted an exemption as referred to in Article 4(4) of Directive 2001/80/EC.
Combustion plants covered by the plan may be exempted from compliance with the emission limit values referred to in Article 30(2) for the pollutants which are subject to the plan or, where applicable, with the rates of desulphurisation referred to in Article 31.
The emission limit values for sulphur dioxide, nitrogen oxides and dust set out in the permit for the combustion plant applicable on 31 December 2015, pursuant in particular to the requirements of Directives 2001/80/EC and 2008/1/EC, shall at least be maintained.
Combustion plants with a total rated thermal input of more than 500 MW firing solid fuels, which were granted the first permit after 1 July 1987, shall comply with the emission limit values for nitrogen oxides set out in Part 1 of Annex V.
For each of the pollutants it covers, the transitional national plan shall set a ceiling defining the maximum total annual emissions for all of the plants covered by the plan on the basis of each plant’s total rated thermal input on 31 December 2010, its actual annual operating hours and its fuel use, averaged over the last 10 years of operation up to and including 2010.
The ceiling for the year 2016 shall be calculated on the basis of the relevant emission limit values set out in Annexes III to VII to Directive 2001/80/EC or, where applicable, on the basis of the rates of desulphurisation set out in Annex III to Directive 2001/80/EC. In the case of gas turbines, the emission limit values for nitrogen oxides set out for such plants in Part B of Annex VI to Directive 2001/80/EC shall be used. The ceilings for the years 2019 and 2020 shall be calculated on the basis of the relevant emission limit values set out in Part 1 of Annex V to this Directive or, where applicable, the relevant rates of desulphurisation set out in Part 5 of Annex V to this Directive. The ceilings for the years 2017 and 2018 shall be set providing a linear decrease of the ceilings between 2016 and 2019.
Where a plant included in the transitional national plan is closed or no longer falls within the scope of Chapter III, this shall not result in an increase in total annual emissions from the remaining plants covered by the plan.
Not later than 1 January 2013, Member States shall communicate their transitional national plans to the Commission.
The Commission shall evaluate the plans and, where the Commission has raised no objections within 12 months of receipt of a plan, the Member State concerned shall consider its plan to be accepted.
When the Commission considers a plan not to be in accordance with the implementing rules established in accordance with Article 41(b), it shall inform the Member State concerned that its plan cannot be accepted. In relation to the evaluation of a new version of a plan which a Member State communicates to the Commission, the time period referred to in the second subparagraph shall be 6 months.
Article 33
Limited life time derogation
During the period from 1 January 2016 to 31 December 2023, combustion plants may be exempted from compliance with the emission limit values referred to in Article 30(2) and with the rates of desulphurisation referred to in Article 31, where applicable, and from their inclusion in the transitional national plan referred to in Article 32 provided that the following conditions are fulfilled:
the operator of the combustion plant undertakes, in a written declaration submitted by 1 January 2014 at the latest to the competent authority, not to operate the plant for more than 17 500 operating hours, starting from 1 January 2016 and ending no later than 31 December 2023;
the operator is required to submit each year to the competent authority a record of the number of operating hours since 1 January 2016;
the emission limit values for sulphur dioxides, nitrogen oxides and dust set out in the permit for the combustion plant applicable on 31 December 2015, pursuant in particular to the requirements of Directives 2001/80/EC and 2008/1/EC, shall at least be maintained during the remaining operational life of the combustion plant. Combustion plants with a total rated thermal input of more than 500 MW firing solid fuels, which were granted the first permit after 1 July 1987, shall comply with the emission limit values for nitrogen oxides set out in Part 1 of Annex V; and
the combustion plant has not been granted an exemption as referred to in Article 4(4) of Directive 2001/80/EC.
Article 34
Small isolated systems
Article 34a
Combustion plants that are part of a small isolated system
The Member States shall take measures to ensure that the emissions are monitored and that no significant pollution is caused. Member States may only exempt installations from the emission limit values when all measures resulting in less pollution have been exhausted. The exemption shall not be made for a longer period than necessary.
Article 35
District heating plants
Until 31 December 2022, a combustion plant may be exempted from compliance with the emission limit values referred to in Article 30(2) and the rates of desulphurisation referred to in Article 31 provided that the following conditions are fulfilled:
the total rated thermal input of the combustion plant does not exceed 200 MW;
the plant was granted a first permit before 27 November 2002 or the operator of that plant had submitted a complete application for a permit before that date, provided that it was put into operation no later than 27 November 2003;
at least 50 % of the useful heat production of the plant, as a rolling average over a period of 5 years, is delivered in the form of steam or hot water to a public network for district heating; and
the emission limit values for sulphur dioxide, nitrogen oxides and dust set out in its permit applicable on 31 December 2015, pursuant in particular to the requirements of Directives 2001/80/EC and 2008/1/EC, are at least maintained until 31 December 2022.
Article 36
Geological storage of carbon dioxide
Member States shall ensure that operators of all combustion plants with a rated electrical output of 300 megawatts or more for which the original construction licence or, in the absence of such a procedure, the original operating licence is granted after the entry into force of Directive 2009/31/EC of the European Parliament and of the Council of 23 April 2009 on the geological storage of carbon dioxide ( 17 ), have assessed whether the following conditions are met:
suitable storage sites are available,
transport facilities are technically and economically feasible,
it is technically and economically feasible to retrofit for carbon dioxide capture.
Article 37
Malfunction or breakdown of the abatement equipment
In the case of a breakdown, the competent authority shall require the operator to reduce or close down operations if a return to normal operation is not achieved within 24 hours, or to operate the plant using low polluting fuels.
The operator shall notify the competent authority within 48 hours after the malfunction or breakdown of the abatement equipment.
The cumulative duration of unabated operation shall not exceed 120 hours in any 12-month period.
The competent authority may grant a derogation from the time limits set out in the first and third subparagraphs in one of the following cases:
there is an overriding need to maintain energy supplies;
the combustion plant with the breakdown would be replaced for a limited period by another plant which would cause an overall increase in emissions.
Article 38
Monitoring of emissions into air
Article 39
Compliance with emission limit values
The emission limit values for air shall be regarded as being complied with if the conditions set out in Part 4 of Annex V are fulfilled.
Article 40
Multi-fuel firing combustion plants
In the case of a multi-fuel firing combustion plant involving the simultaneous use of two or more fuels, the competent authority shall set the emission limit values in accordance with the following steps:
taking the emission limit value relevant for each individual fuel and pollutant corresponding to the total rated thermal input of the entire combustion plant as set out in Parts 1 and 2 of Annex V;
determining fuel-weighted emission limit values, which are obtained by multiplying the individual emission limit value referred to in point (a) by the thermal input delivered by each fuel, and dividing the product of multiplication by the sum of the thermal inputs delivered by all fuels,
aggregating the fuel-weighted emission limit values.
In the case of multi-fuel firing combustion plants covered by Article 30(2), which use the distillation and conversion residues from the refining of crude-oil for own consumption, alone or with other fuels, the following emission limit values may be applied instead of the emission limit values set according to paragraph 1:
where, during the operation of the combustion plant, the proportion contributed by the determinative fuel to the sum of the thermal inputs delivered by all fuels is 50 % or more, the emission limit value set in Part 1 of Annex V for the determinative fuel;
where the proportion contributed by the determinative fuel to the sum of the thermal inputs delivered by all fuels is less than 50 %, the emission limit value determined in accordance with the following steps:
taking the emission limit values set out in Part 1 of Annex V for each of the fuels used, corresponding to the total rated thermal input of the combustion plant;
calculating the emission limit value of the determinative fuel by multiplying the emission limit value, determined for that fuel according to point (i), by a factor of two, and subtracting from this product the emission limit value of the fuel used with the lowest emission limit value as set out in Part 1 of Annex V, corresponding to the total rated thermal input of the combustion plant;
determining the fuel-weighted emission limit value for each fuel used by multiplying the emission limit value determined under points (i) and (ii) by the thermal input of the fuel concerned and by dividing the product of this multiplication by the sum of the thermal inputs delivered by all fuels;
aggregating the fuel-weighted emission limit values determined under point (iii).
Article 41
Implementing rules
Implementing rules shall be established concerning:
the determination of the start-up and shut-down periods referred to in point 27 of Article 3 and in point 1 of Part 4 of Annex V; and
the transitional national plans referred to in Article 32 and, in particular, the setting of emission ceilings and related monitoring and reporting.
Those implementing rules shall be adopted in accordance with the regulatory procedure referred to in Article 75(2). The Commission shall make appropriate proposals not later than 7 July 2011.
CHAPTER IV
SPECIAL PROVISIONS FOR WASTE INCINERATION PLANTS AND WASTE CO-INCINERATION PLANTS
Article 42
Scope
This Chapter shall apply to waste incineration plants and waste co-incineration plants which incinerate or co-incinerate solid or liquid waste.
This Chapter shall not apply to gasification or pyrolysis plants, if the gases or liquids resulting from such thermal treatment of waste are treated prior to their incineration to such an extent that:
the incineration causes emissions lower than the combustion of the least polluting fuels available on the market that could be combusted in the installation;
for emissions other than nitrogen oxides, sulphur oxides and dust, the incineration does not cause emissions higher than those from incineration or co-incineration of waste.
For the purposes of this Chapter, waste incineration plants and waste co-incineration plants shall include all incineration lines or co-incineration lines, waste reception, storage, on site pretreatment facilities, waste-, fuel- and air-supply systems, boilers, facilities for the treatment of waste gases, on-site facilities for treatment or storage of residues and waste water, stacks, devices and systems for controlling incineration or co-incineration operations, recording and monitoring incineration or co-incineration conditions.
If processes other than oxidation, such as pyrolysis, gasification or plasma process, are applied for the thermal treatment of waste, the waste incineration plant or waste co-incineration plant shall include both the thermal treatment process and the subsequent incineration process.
If waste co-incineration takes place in such a way that the main purpose of the plant is not the generation of energy or production of material products but rather the thermal treatment of waste, the plant shall be regarded as a waste incineration plant.
This Chapter shall not apply to the following plants:
plants treating only the following wastes:
waste listed in point (b) of point 31 of Article 3;
radioactive waste;
animal carcasses as regulated by Regulation (EC) No 1774/2002 of the European Parliament and of the Council of 3 October 2002 laying down health rules concerning animal by-products not intended for human consumption ( 18 );
waste resulting from the exploration for, and the exploitation of, oil and gas resources from off-shore installations and incinerated on board the installations;
experimental plants used for research, development and testing in order to improve the incineration process and which treat less than 50 tonnes of waste per year.
Article 43
Definition of residue
For the purposes of this Chapter, ‘residue’ shall mean any liquid or solid waste which is generated by a waste incineration plant or waste co-incineration plant.
Article 44
Applications for permits
An application for a permit for a waste incineration plant or waste co-incineration plant shall include a description of the measures which are envisaged to guarantee that the following requirements are met:
the plant is designed, equipped and will be maintained and operated in such a manner that the requirements of this Chapter are met taking into account the categories of waste to be incinerated or co-incinerated;
the heat generated during the incineration and co-incineration process is recovered as far as practicable through the generation of heat, steam or power;
the residues will be minimised in their amount and harmfulness and recycled where appropriate;
the disposal of the residues which cannot be prevented, reduced or recycled will be carried out in conformity with national and Union law.
Article 45
Permit conditions
The permit shall include the following:
a list of all types of waste which may be treated using at least the types of waste set out in the European Waste List established by Decision 2000/532/EC, if possible, and containing information on the quantity of each type of waste, where appropriate;
the total waste incinerating or co-incinerating capacity of the plant;
the limit values for emissions into air and water;
the requirements for the pH, temperature and flow of waste water discharges;
the sampling and measurement procedures and frequencies to be used to comply with the conditions set for emission monitoring;
the maximum permissible period of any technically unavoidable stoppages, disturbances, or failures of the purification devices or the measurement devices, during which the emissions into the air and the discharges of waste water may exceed the prescribed emission limit values.
In addition to the requirements set out in paragraph 1, the permit granted to a waste incineration plant or waste co-incineration plant using hazardous waste shall include the following:
a list of the quantities of the different categories of hazardous waste which may be treated;
the minimum and maximum mass flows of those hazardous wastes, their lowest and maximum calorific values and their maximum contents of polychlorinated biphenyls, pentachlorophenol, chlorine, fluorine, sulphur, heavy metals and other polluting substances.
Article 46
Control of emissions
Emissions into air from waste incineration plants and waste co-incineration plants shall not exceed the emission limit values set out in parts 3 and 4 of Annex VI or determined in accordance with Part 4 of that Annex.
If in a waste co-incineration plant more than 40 % of the resulting heat release comes from hazardous waste, or the plant co-incinerates untreated mixed municipal waste, the emission limit values set out in Part 3 of Annex VI shall apply.
The emission limit values shall apply at the point where waste waters from the cleaning of waste gases are discharged from the waste incineration plant or waste co-incineration plant.
When waste waters from the cleaning of waste gases are treated outside the waste incineration plant or waste co-incineration plant at a treatment plant intended only for the treatment of this sort of waste water, the emission limit values set out in Part 5 of Annex VI shall be applied at the point where the waste waters leave the treatment plant. Where the waste water from the cleaning of waste gases is treated collectively with other sources of waste water, either on site or off site, the operator shall make the appropriate mass balance calculations, ►C1 using the results of the measurements set out in point 3 of Part 6 of Annex VI in order to determine the emission levels in the final waste water discharge ◄ that can be attributed to the waste water arising from the cleaning of waste gases.
Under no circumstances shall dilution of waste water take place for the purpose of complying with the emission limit values set out in Part 5 of Annex VI.
Waste incineration plant sites and waste co-incineration plant sites, including associated storage areas for waste, shall be designed and operated in such a way as to prevent the unauthorised and accidental release of any polluting substances into soil, surface water and groundwater.
Storage capacity shall be provided for contaminated rainwater run-off from the waste incineration plant site or waste co-incineration plant site or for contaminated water arising from spillage or fire-fighting operations. The storage capacity shall be adequate to ensure that such waters can be tested and treated before discharge where necessary.
Without prejudice to Article 50(4)(c), the waste incineration plant or waste co-incineration plant or individual furnaces being part of a waste incineration plant or waste co-incineration plant shall under no circumstances continue to incinerate waste for a period of more than 4 hours uninterrupted where emission limit values are exceeded.
The cumulative duration of operation in such conditions over 1 year shall not exceed 60 hours.
The time limit set out in the second subparagraph shall apply to those furnaces which are linked to one single waste gas cleaning device.
Article 47
Breakdown
In the case of a breakdown, the operator shall reduce or close down operations as soon as practicable until normal operations can be restored.
Article 48
Monitoring of emissions
Emissions to air from waste incineration and co-incineration plants shall also be monitored during other than normal operating conditions. Emissions during start-up and shutdown while no waste is being incinerated, including emissions of PCDD/F and dioxin-like PCBs, shall be estimated based on measurement campaigns, carried out at regular intervals, such as every three years, carried out during planned start-up or shutdown operations. Emissions of PCDD/F and dioxin-like PCBs shall as far as possible be prevented or minimised.
Article 49
Compliance with emission limit values
The emission limit values for air and water shall be regarded as being complied with if the conditions described in Part 8 of Annex VI are fulfilled.
Article 50
Operating conditions
Waste incineration plants shall be designed, equipped, built and operated in such a way that the gas resulting from the incineration of waste is raised, after the last injection of combustion air, in a controlled and homogeneous fashion and even under the most unfavourable conditions, to a temperature of at least 850 °C for at least two seconds.
Waste co-incineration plants shall be designed, equipped, built and operated in such a way that the gas resulting from the co-incineration of waste is raised in a controlled and homogeneous fashion and even under the most unfavourable conditions, to a temperature of at least 850 °C for at least two seconds.
If hazardous waste with a content of more than 1 % of halogenated organic substances, expressed as chlorine, is incinerated or co-incinerated, the temperature required to comply with the first and second subparagraphs shall be at least 1 100 °C.
In waste incineration plants, the temperatures set out in the first and third subparagraphs shall be measured near the inner wall of the combustion chamber. The competent authority may authorise the measurements at another representative point of the combustion chamber.
Each combustion chamber of a waste incineration plant shall be equipped with at least one auxiliary burner. This burner shall be switched on automatically when the temperature of the combustion gases after the last injection of combustion air falls below the temperatures set out in paragraph 2. It shall also be used during plant start-up and shut-down operations in order to ensure that those temperatures are maintained at all times during these operations and as long as unburned waste is in the combustion chamber.
The auxiliary burner shall not be fed with fuels which can cause higher emissions than those resulting from the burning of gas oil as defined in Article 2(2) of Council Directive 1999/32/EC of 26 April 1999 relating to a reduction in the sulphur content of certain liquid fuels ( 19 ), liquefied gas or natural gas.
Waste incineration plants and waste co-incineration plants shall operate an automatic system to prevent waste feed in the following situations:
at start-up, until the temperature set out in paragraph 2 of this Article or the temperature specified in accordance with Article 51(1) has been reached;
whenever the temperature set out in paragraph 2 of this Article or the temperature specified in accordance with Article 51(1) is not maintained;
whenever the continuous measurements show that any emission limit value is exceeded due to disturbances or failures of the waste gas cleaning devices.
Article 51
Authorisation to change operating conditions
Emissions of total organic carbon and carbon monoxide from waste co-incineration plants, authorised to change operating conditions according to paragraph 1 shall also comply with the emission limit values set out in Part 3 of Annex VI.
Emissions of total organic carbon from bark boilers within the pulp and paper industry co-incinerating waste at the place of its production which were in operation and had a permit before 28 December 2002 and which are authorised to change operating conditions according to paragraph 1 shall also comply with the emission limit values set out in Part 3 of Annex VI.
Article 52
Delivery and reception of waste
Prior to accepting hazardous waste at the waste incineration plant or waste co-incineration plant, the operator shall collect available information about the waste for the purpose of verifying compliance with the permit requirements specified in Article 45(2).
That information shall cover the following:
all the administrative information on the generating process contained in the documents mentioned in paragraph 4(a);
the physical, and as far as practicable, chemical composition of the waste and all other information necessary to evaluate its suitability for the intended incineration process;
the hazardous characteristics of the waste, the substances with which it cannot be mixed, and the precautions to be taken in handling the waste.
Prior to accepting hazardous waste at the waste incineration plant or waste co-incineration plant, at least the following procedures shall be carried out by the operator:
the checking of the documents required by Directive 2008/98/EC and, where applicable, those required by Regulation (EC) No 1013/2006 of the European Parliament and of the Council of 14 June 2006 on shipments of waste ( 20 ) and by legislation on transport of dangerous goods;
the taking of representative samples, unless inappropriate as far as possible before unloading, to verify conformity with the information provided for in paragraph 3 by carrying out controls and to enable the competent authorities to identify the nature of the wastes treated.
The samples referred to in point (b) shall be kept for at least 1 month after the incineration or co-incineration of the waste concerned.
Article 53
Residues
Article 54
Substantial change
A change of operation of a waste incineration plant or a waste co-incineration plant treating only non-hazardous waste in an installation covered by Chapter II which involves the incineration or co-incineration of hazardous waste shall be regarded as a substantial change.
Article 55
Reporting and public information on waste incineration plants and waste co-incineration plants
CHAPTER V
SPECIAL PROVISIONS FOR INSTALLATIONS AND ACTIVITIES USING ORGANIC SOLVENTS
Article 56
Scope
This chapter shall apply to activities listed in Part 1 of Annex VII and, where applicable, reaching the consumption thresholds set out in Part 2 of that Annex.
Article 57
Definitions
For the purposes of this Chapter, the following definitions shall apply:
‘existing installation’ means an installation in operation on 29 March 1999 or which was granted a permit or registered before 1 April 2001 or the operator of which submitted a complete application for a permit before 1 April 2001, provided that that installation was put in operation no later than 1 April 2002;
‘waste gases’ means the final gaseous discharge containing volatile organic compounds or other pollutants from a stack or abatement equipment into air;
‘fugitive emissions’ means any emissions not in waste gases of volatile organic compounds into air, soil and water as well as solvents contained in any products, unless otherwise stated in Part 2 of Annex VII;
‘total emissions’ means the sum of fugitive emissions and emissions in waste gases;
‘mixture’ means mixture as defined in Article 3(2) of Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006 concerning the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH) and establishing a European Chemicals Agency ( 21 ),
‘adhesive’ means any mixture, including all the organic solvents or mixtures containing organic solvents necessary for its proper application, which is used to adhere separate parts of a product;
‘ink’ means a mixture, including all the organic solvents or mixtures containing organic solvents necessary for its proper application, which is used in a printing activity to impress text or images on to a surface;
‘varnish’ means a transparent coating;
‘consumption’ means the total input of organic solvents into an installation per calendar year, or any other 12-month period, less any volatile organic compounds that are recovered for re-use;
‘input’ means the quantity of organic solvents and their quantity in mixtures used when carrying out an activity, including the solvents recycled inside and outside the installation, and which are counted every time they are used to carry out the activity;
‘re-use’ means the use of organic solvents recovered from an installation for any technical or commercial purpose and including use as a fuel but excluding the final disposal of such recovered organic solvent as waste;
‘contained conditions’ means conditions under which an installation is operated so that the volatile organic compounds released from the activity are collected and discharged in a controlled way either via a stack or abatement equipment and are, therefore, not entirely fugitive;
‘start-up and shut-down operations’ means operations excluding regularly oscillating activity phases whilst bringing an activity, an equipment item or a tank into or out of service or into or out of an idling state.
Article 58
Substitution of hazardous substances
Substances or mixtures which, because of their content of volatile organic compounds classified as carcinogens, mutagens, or toxic to reproduction under Regulation (EC) No 1272/2008, are assigned or need to carry the hazard statements H340, H350, H350i, H360D or H360F, shall be replaced, as far as possible by less harmful substances or mixtures within the shortest possible time.
Article 59
Control of emissions
Member States shall take the necessary measures to ensure that each installation complies with either of the following:
the emission of volatile organic compounds from installations shall not exceed the emission limit values in waste gases and the fugitive emission limit values, or the total emission limit values, and other requirements laid down in Parts 2 and 3 of Annex VII are complied with;
the requirements of the reduction scheme set out in Part 5 of Annex VII provided that an equivalent emission reduction is achieved compared to that achieved through the application of the emission limit values referred to in point (a).
Member States shall report to the Commission in accordance with Article 72(1) on the progress in achieving the equivalent emission reduction referred to in point (b).
Installations where two or more activities are carried out, each of which exceeds the thresholds in Part 2 of Annex VII shall:
as regards the substances specified in paragraph 5, meet the requirements of that paragraph for each activity individually;
as regards all other substances, either:
meet the requirements of paragraph 1 for each activity individually; or
have total emissions of volatile organic compounds not exceeding those which would have resulted had point (i) been applied.
Article 60
Monitoring of emissions
Member States shall, either by specification in the permit conditions or by general binding rules, ensure that measurements of emissions are carried out in accordance with Part 6 of Annex VII.
Article 61
Compliance with emission limit values
The emission limit values in waste gases shall be regarded as being complied with if the conditions set out in Part 8 of Annex VII are fulfilled.
Article 62
Reporting on compliance
The operator shall supply the competent authority, on request, with data enabling the competent authority to verify compliance with either of the following:
emission limit values in waste gases, fugitive emission limit values and total emission limit values;
the requirements of the reduction scheme under Part 5 of Annex VII;
the derogations granted in accordance with Article 59(2) and (3).
This may include a solvent management plan prepared in accordance with Part 7 of Annex VII.
Article 63
Substantial change to existing installations
A change of the maximum mass input of organic solvents by an existing installation averaged over 1 day, where the installation is operated at its design output under conditions other than start-up and shut-down operations and maintenance of equipment, shall be considered as substantial if it leads to an increase of emissions of volatile organic compounds of more than:
25 % for an installation carrying out either activities which fall within the lower threshold band of items 1, 3, 4, 5, 8, 10, 13, 16 or 17 of the table in Part 2 of Annex VII or, activities which fall under one of the other items of Part 2 of Annex VII, and with a solvent consumption of less than 10 tonnes per year;
10 % for all other installations.
Article 64
Exchange of information on substitution of organic solvents
The Commission shall organise an exchange of information with the Member States, the industry concerned and non-governmental organisations promoting environmental protection on the use of organic solvents and their potential substitutes and techniques which have the least potential effects on air, water, soil, ecosystems and human health.
The exchange of information shall be organised on all of the following:
fitness for use;
potential effects on human health and occupational exposure in particular;
potential effects on the environment;
the economic consequences, in particular the costs and benefits of the options available.
Article 65
Access to information
The decision of the competent authority, including at least a copy of the permit, and any subsequent updates, shall be made available to the public.
The general binding rules applicable for installations and the list of installations subject to permitting and registration shall be made available to the public.
CHAPTER VI
SPECIAL PROVISIONS FOR INSTALLATIONS PRODUCING TITANIUM DIOXIDE
Article 66
Scope
This Chapter shall apply to installations producing titanium dioxide.
Article 67
Prohibition of the disposal of waste
Member States shall prohibit the disposal of the following waste into any water body, sea or ocean:
solid waste;
the mother liquors arising from the filtration phase following hydrolysis of the titanyl sulphate solution from installations applying the sulphate process; including the acid waste associated with such liquors, containing overall more than 0,5 % free sulphuric acid and various heavy metals and including such mother liquors which have been diluted until they contain 0,5 % or less free sulphuric acid;
waste from installations applying the chloride process containing more than 0,5 % free hydrochloric acid and various heavy metals, including such waste which has been diluted until it contains 0,5 % or less free hydrochloric acid;
filtration salts, sludges and liquid waste arising from the treatment (concentration or neutralisation) of the waste mentioned under points (b) and (c) and containing various heavy metals, but not including neutralised and filtered or decanted waste containing only traces of heavy metals and which, before any dilution, has a pH value above 5,5.
Article 68
Control of emissions into water
Emissions from installations into water shall not exceed the emission limit values set out in Part 1 of Annex VIII.
Article 69
Prevention and control of emissions into air
Article 70
Monitoring of emissions
CHAPTER VIA
SPECIAL PROVISIONS FOR REARING POULTRY AND PIGS
Article 70a
Scope
This Chapter shall apply to the activities set out in Annex Ia which reach the capacity thresholds set out in that Annex.
Article 70b
Aggregation rule
Member States shall ensure that the rule referred to in the first subparagraph is not used to circumvent the obligations set out in this Directive.
Article 70c
Permits and registrations
Member States may use any similar pre-existing procedure for the registration of installations in order to avoid creating an administrative burden.
Member States may apply a permitting procedure to the intensive rearing of poultry and pigs:
with more than 40 000 places for poultry;
with more than 2 000 places for production pigs over 30 kg; or
with more than 750 places for sows.
Member States may include requirements for certain categories of installations falling within the scope of this Chapter in the general binding rules referred to in Article 6.
Member States shall specify the procedure for registration or granting a permit in respect of installations falling within the scope of this Chapter. Those procedures shall include at least the information listed in paragraph 2.
Registrations or applications for permits shall include at least a description of the following elements:
the installation and its activities;
the animal type;
the stocking density in LSU per hectare calculated in accordance with Annex Ia, where necessary;
the capacity of the installation;
the sources of emissions from the installation;
the nature and quantities of foreseeable emissions from the installation into each medium.
Article 70d
Obligations of the operator
Monitoring data shall be obtained by means of measurement methods or, where not practicable, by calculation methods such as the use of emission factors. The methods used for obtaining the monitoring data shall be described in the operating rules.
The operator shall keep a record of, and process, all monitoring results, for a period of at least 5 years, in such a way as to enable the verification of compliance with the emission limit values and environmental performance limit values set out in operating rules.
Article 70e
Monitoring
Article 70f
Non-compliance
Where non-compliance causes a significant degradation of local air, water or soil conditions, or where it poses, or risks posing, a significant danger to human health, the operation of the installation shall be suspended by the competent authority until compliance is restored.
Article 70g
Public information and participation
Member States shall ensure that the public concerned are given early and effective opportunities to participate in the following procedures:
preparation of general binding rules as referred to in Article 6 on permits for installations falling within the scope of this Chapter;
the granting of a permit for a new installation falling within the scope of this Chapter;
the granting of an updated permit in accordance with Article 70c(4) for any substantial change to an existing installation falling within the scope of this Chapter; or
the procedure for registration, in the event that general binding rules are not adopted, and the Member States allow the installation only to be registered.
The competent authority shall make available to the public, including systematically via the internet, free of charge and without restricting access to registered users, the following documents and information:
the permit or the registration;
the results of the consultations held in accordance with paragraph 1;
the general binding rules referred to in Article 6 which are applicable to installations falling within the scope of this Chapter; and
the reports of inspections of the installations falling within the scope of this Chapter.
Article 70h
Access to justice
Member States shall ensure that, in accordance with the relevant national legal system, members of the public concerned have access to a review procedure before a court of law or another independent and impartial body established by law to challenge the substantive or procedural legality of decisions, acts or omissions subject to this Chapter when one of the following conditions is met:
they have a sufficient interest;
they maintain the impairment of a right, where administrative procedural law of a Member State requires that as a precondition.
Standing in the review procedure shall not be conditional on the role that the member of the public concerned played during a participatory phase of the decision-making procedures under this Directive.
The review procedure shall be fair, equitable, timely and not prohibitively expensive, and shall provide for adequate and effective remedies, including injunctive relief as appropriate.
Article 70i
Uniform conditions for operating rules
The Commission shall organise an exchange of information between Member States, the sectors concerned, non-governmental organisations promoting environmental protection and the Commission before establishing uniform conditions for operating rules in accordance with paragraph 2. The exchange of information shall, in particular, address the following:
the emission and environmental performance levels of installations and techniques, and other measures consistent with Annex III;
the techniques used, associated monitoring, cross-media effects, economic and technical viability and developments in that regard;
best available techniques identified after considering the issues mentioned in points (a) and (b);
emerging techniques.
The uniform conditions for operating rules shall be consistent with the use of best available techniques for the activities listed in Annex Ia and shall take into account the nature, type, size and stocking density of those installations, the size of herds of single animal types in mixed farms, and the specificities of pasture-based rearing systems, where animals are only seasonally reared in indoor installations. They shall also include indicative information on emerging techniques, where available.
That implementing act shall be adopted in accordance with the examination procedure referred to in Article 75(2).
CHAPTER VII
COMMITTEE, TRANSITIONAL AND FINAL PROVISIONS
Article 71
Competent authorities
Member States shall designate the competent authorities responsible for carrying out the obligations arising from this Directive.
Article 72
Reporting by Member States
For all combustion plants covered by Chapter III of this Directive, Member States shall, from 1 January 2016, establish an annual inventory of the sulphur dioxide, nitrogen oxides and dust emissions and energy input.
Taking into account the aggregation rules set out in Article 29, the competent authority shall obtain the following data for each combustion plant:
the total rated thermal input (MW) of the combustion plant;
the type of combustion plant: boiler, gas turbine, gas engine, diesel engine, other (specifying the type);
the date of the start of operation of the combustion plant;
the total annual emissions (tonnes per year) of sulphur dioxide, nitrogen oxides and dust (as total suspended particles);
the number of operating hours of the combustion plant;
the total annual amount of energy input, related to the net calorific value (TJ per year), broken down in terms of the following categories of fuel: coal, lignite, biomass, peat, other solid fuels (specifying the type), liquid fuels, natural gas, other gases (specifying the type).
The annual plant-by-plant data contained in these inventories shall be made available to the Commission upon request.
A summary of the inventories shall be made available to the Commission every 3 years within 12 months from the end of the three-year period considered. This summary shall show separately the data for combustion plants within refineries.
The Commission shall make available to the Member States and to the public a summary of the comparison and evaluation of those inventories in accordance with Directive 2003/4/EC within 24 months from the end of the three-year period considered.
Member States shall, from 1 January 2016, report the following data annually to the Commission:
for combustion plants to which Article 31 applies, the sulphur content of the indigenous solid fuel used and the rate of desulphurisation achieved, averaged over each month. For the first year where Article 31 is applied, the technical justification of the non-feasibility of complying with the emission limit values referred to in Article 30(2) and (3) shall also be reported; and
for combustion plants which do not operate more than 1 500 operating hours per year as a rolling average over a period of 5 years, the number of operating hours per year.
Article 73
Review
By 30 June 2028 and every 5 years thereafter, the Commission shall submit to the European Parliament and to the Council a report reviewing the implementation of this Directive. The report shall include information on activities for which BAT conclusions have or have not been adopted pursuant to Article 13(5) of this Directive, take into account the dynamics of innovation, including emerging techniques, the need for further pollution prevention measures and the review referred to in Article 8 of Directive 2003/87/EC.
That report shall include an assessment of the need for Union action through the establishment or updating of Union-wide minimum requirements for emission limit values and for rules on monitoring and compliance for activities within the scope of the BAT conclusions adopted during the previous five-year period, on the basis of the following criteria:
the impact of the activities concerned on the environment as a whole and on human health;
the state of implementation of best available techniques for the activities concerned.
That assessment shall consider the opinion of the forum referred to in Article 13(4).
Chapter III and Annex V of this Directive shall be considered to represent the Union-wide minimum requirements in the case of large combustion plants.
The report shall be accompanied by a legislative proposal where appropriate. Where the assessment referred to in the second subparagraph identifies such a need, the legislative proposal shall include provisions establishing or updating Union-wide minimum requirements for emission limit values and for rules on monitoring and compliance assessment for the activities concerned.
The Commission shall, by 31 December 2012, review the need to control emissions from:
the combustion of fuels in installations with a total rated thermal input below 50 MW;
the intensive rearing of cattle; and
the spreading of manure.
The Commission shall report the results of that review to the European Parliament and to the Council accompanied by a legislative proposal where appropriate.
The Commission shall, using an evidence-based methodology and taking into account the specificities of the sector, assess the need for Union action to:
comprehensively address the emissions from the rearing of livestock within the Union, in particular from cattle; and
further achieve the objective of global environmental protection with respect to products placed on the Union market, through the prevention and control of emissions from livestock farming, and in a manner consistent with the Union’s international obligations.
The Commission shall report the results of that assessment by 31 December 2026 to the European Parliament and the Council. The report shall be accompanied by a legislative proposal where appropriate.
The Commission shall review:
the need to control emissions from onshore and offshore exploration and production of mineral oil and gas;
the need to control emissions from the on-site treatment and extraction of non-energy industrial minerals used in industry other than for construction, as well as the need to control emissions from the on-site treatment and extraction of ores which are newly carried out in the Union;
the need to revise the activity threshold in Annex I for the production of hydrogen by electrolysis of water.
The Commission shall include the results of that review in the first of the reports to the European Parliament and to the Council required under the first paragraph.
Article 74
Amendments of Annexes
The Commission shall make public relevant studies and analyses used in the preparation of a delegated act adopted in accordance with this Article, at the latest upon the adoption of the delegated act.
Article 75
Committee procedure
Article 76
Exercise of the delegation
▼M1 —————
Article 79
Penalties
For the most serious infringements committed by a legal person, the maximum amount of the administrative financial penalties referred to in the first subparagraph shall be at least 3 % of the annual Union turnover of the operator in the financial year preceding the year in which the fine is imposed.
Member States may also, or alternatively, use criminal penalties, provided that they are equivalently effective, proportionate and dissuasive to the administrative financial penalties referred to in this Article.
Member States shall ensure that the penalties established pursuant to this Article give due regard to the following, as applicable:
the nature, gravity, and extent of the infringement;
the population or the environment affected by the infringement, bearing in mind the impact of the infringement on the objective of achieving a high level of protection of human health and the environment;
the repetitive or one-off character of the infringement.
Article 79a
Compensation
Article 80
Transposition
Member States shall bring into force the laws, regulations and administrative provisions necessary to comply with Article 2, points (8), (11) to (15), (18) to (23), (26) to (30), (34) to (38) and (41) of Article 3, Article 4(2) and (3), Article 7, Articles 8 and 10, Article 11(e) and (h), Article 12(1)(e) and (h), Article 13(7), point (ii) of Article 14(1)(c), points (d), (e), (f) and (h) of Article 14(1), Article 14(2) to (7), Article 15(2) to (5), Articles 16, 17 and 19, Article 21(2) to (5), Articles 22, 23, 24, 27, 28 and 29, Article 30(1), (2), (3), (4), (7) and (8), Articles 31, 32, 33, 34, 35, 36, 38 and 39, Article 40(2) and (3), Articles 42 and 43, Article 45(1), Article 58, Article 59(5), Article 63, Article 65(3), Articles 69, 70, 71, 72 and 79, and with the first subparagraph and points 1.1, 1.4, 2.5(b), 3.1, 4, 5, 6.1(c), 6.4(b), 6.10 and 6.11 of Annex I, Annex II, point 12 of Annex III, Annex V, point (b) of Part 1, points 2.2, 2.4, 3.1 and 3.2 of Part 4, points 2.5 and 2.6 of Part 6 and point 1.1(d) of Part 8 of Annex VI, point 2 of Part 4, point 1 of Part 5, point 3 of Part 7 of Annex VII, points 1 and 2(c) of Part 1, points 2 and 3 of Part 2 and Part 3 of Annex VIII by 7 January 2013.
They shall apply those measures from that same date.
When Member States adopt those measures, they shall contain a reference to this Directive or be accompanied by such a reference on the occasion of their official publication. The methods of making such reference shall be laid down by Member States.
Article 81
Repeal
Article 82
Transitional provisions
Point 3.2 of Part 4 of Annex VI shall apply in relation to combustion plants which co-incinerate waste, as from:
1 January 2016, for combustion plants referred to in Article 30(2)
7 January 2013, for combustion plants referred to in Article 30(3).
Article 83
Entry into force
This Directive shall enter into force on the 20th day following its publication in the Official Journal of the European Union.
Article 84
Addressees
This Directive is addressed to the Member States.
ANNEX I
Categories of activities referred to in Article 10
The threshold values given below generally refer to production capacities or outputs. Where several activities falling under the same activity description containing a threshold are operated in the same installation, the capacities of such activities are added together. For waste management activities, this calculation shall apply at the level of activities 5.1, 5.3(a) and 5.3(b).
The Commission shall establish guidance on:
the relationship between waste management activities described in this Annex and those described in Annexes I and II to Directive 2008/98/EC; and
the interpretation of the term ‘industrial scale’ regarding the description of chemical industry activities described in this Annex.
1. Energy industries
|
1.1. |
Combustion of fuels in installations with a total rated thermal input of 50 MW or more |
|
1.2. |
Refining of mineral oil and gas |
|
1.3. |
Production of coke |
|
1.4. |
Gasification, liquefaction or pyrolysis of:
(a)
coal;
(b)
other fuels in installations with a total rated thermal input of 20 MW or more. |
2. Production and processing of metals
|
2.1. |
Metal ore (including sulphide ore) roasting or sintering |
|
2.2. |
Production of pig iron or steel (primary or secondary fusion) including continuous casting, with a capacity exceeding 2,5 tonnes per hour |
|
2.3. |
Processing of ferrous metals:
(a)
operation of hot-rolling mills with a capacity exceeding 20 tonnes of crude steel per hour;
(aa)
operation of cold-rolling mills with a capacity exceeding 10 tonnes of crude steel per hour;
(b)
operation of smitheries with hammers the energy of which exceeds 50 kilojoule per hammer;
(ba)
operation of smitheries with forging presses the force of which exceeds 30 mega-newton (MN) per press;
(c)
application of protective fused metal coats with an input exceeding 2 tonnes of crude steel per hour. |
|
2.4. |
Operation of ferrous metal foundries with a production capacity exceeding 20 tonnes per day |
|
2.5. |
Processing of non-ferrous metals:
(a)
production of non-ferrous crude metals from ore, concentrates or secondary raw materials by metallurgical, chemical or electrolytic processes;
(b)
melting, including the alloyage, of non-ferrous metals, including recovered products and operation of non-ferrous metal foundries, with a melting capacity exceeding 4 tonnes per day for lead and cadmium or 20 tonnes per day for all other metals. |
|
2.6. |
Surface treatment of metals or plastic materials using an electrolytic or chemical process where the volume of the treatment vats exceeds 30 m3 |
|
2.7. |
Manufacture of batteries, other than exclusively assembling, with a production capacity of 15 000 tonnes of battery cells (cathode, anode, electrolyte, separator, capsule) or more per year. |
3. Mineral industry
|
3.1. |
Production of cement, lime and magnesium oxide:
(a)
production of cement clinker in rotary kilns with a production capacity exceeding 500 tonnes per day or in other kilns with a production capacity exceeding 50 tonnes per day;
(b)
production of lime in kilns with a production capacity exceeding 50 tonnes per day;
(c)
production of magnesium oxide in kilns with a production capacity exceeding 50 tonnes per day. |
|
3.2. |
Production of asbestos or the manufacture of asbestos-based products |
|
3.3. |
Manufacture of glass including glass fibre with a melting capacity exceeding 20 tonnes per day |
|
3.4. |
Melting mineral substances including the production of mineral fibres with a melting capacity exceeding 20 tonnes per day |
|
3.5. |
Manufacture of ceramic products by firing, in particular roofing tiles, bricks, refractory bricks, tiles, stoneware or porcelain with:
(a)
a production capacity exceeding 75 tonnes per day; and/or
(b)
a kiln capacity exceeding 4 m3 and a setting density per kiln exceeding 300 kg/m3. |
|
3.6. |
Extraction including on-site treatment operations, such as comminution, size control, beneficiation and upgrading, of the following ores on an industrial scale: bauxite, chromium, cobalt, copper, gold, iron, lead, lithium, manganese, nickel, palladium, platinum, tin, tungsten and zinc. |
4. Chemical industry
For the purpose of this section, production within the meaning of the categories of activities contained in this section means the production on an industrial scale by chemical or biological processing of substances or groups of substances listed in points 4.1 to 4.6
|
4.1. |
Production of organic chemicals, such as:
(a)
simple hydrocarbons (linear or cyclic, saturated or unsaturated, aliphatic or aromatic);
(b)
oxygen-containing hydrocarbons such as alcohols, aldehydes, ketones, carboxylic acids, esters and mixtures of esters, acetates, ethers, peroxides and epoxy resins;
(c)
sulphurous hydrocarbons;
(d)
nitrogenous hydrocarbons such as amines, amides, nitrous compounds, nitro compounds or nitrate compounds, nitriles, cyanates, isocyanates;
(e)
phosphorus-containing hydrocarbons;
(f)
halogenic hydrocarbons;
(g)
organometallic compounds;
(h)
plastic materials (polymers, synthetic fibres and cellulose-based fibres);
(i)
synthetic rubbers;
(j)
dyes and pigments;
(k)
surface-active agents and surfactants. |
|
4.2. |
Production of inorganic chemicals, such as:
(a)
gases, such as ammonia, chlorine or hydrogen chloride, fluorine or hydrogen fluoride, carbon oxides, sulphur compounds, nitrogen oxides, hydrogen except when produced by electrolysis of water, sulphur dioxide, carbonyl chloride;
(b)
acids, such as chromic acid, hydrofluoric acid, phosphoric acid, nitric acid, hydrochloric acid, sulphuric acid, oleum, sulphurous acids;
(c)
bases, such as ammonium hydroxide, potassium hydroxide, sodium hydroxide;
(d)
salts, such as ammonium chloride, potassium chlorate, potassium carbonate, sodium carbonate, perborate, silver nitrate;
(e)
non-metals, metal oxides or other inorganic compounds such as calcium carbide, silicon, silicon carbide. |
|
4.3. |
Production of phosphorous-, nitrogen- or potassium-based fertilisers (simple or compound fertilisers) |
|
4.4. |
Production of plant protection products or of biocides |
|
4.5. |
Production of pharmaceutical products including intermediates |
|
4.6. |
Production of explosives |
5. Waste management
|
5.1. |
Disposal or recovery of hazardous waste with a capacity exceeding 10 tonnes per day involving one or more of the following activities:
(a)
biological treatment;
(b)
physico-chemical treatment;
(c)
blending or mixing prior to submission to any of the other activities listed in points 5.1 and 5.2;
(d)
repackaging prior to submission to any of the other activities listed in points 5.1 and 5.2;
(e)
solvent reclamation/regeneration;
(f)
recycling/reclamation of inorganic materials other than metals or metal compounds;
(g)
regeneration of acids or bases;
(h)
recovery of components used for pollution abatement;
(i)
recovery of components from catalysts;
(j)
oil re-refining or other reuses of oil;
(k)
surface impoundment. |
|
5.2. |
Disposal or recovery of waste in waste incineration plants or in waste co-incineration plants:
(a)
for non-hazardous waste with a capacity exceeding 3 tonnes per hour;
(b)
for hazardous waste with a capacity exceeding 10 tonnes per day. |
|
5.3. |
(a)
Disposal of non-hazardous waste with a capacity exceeding 50 tonnes per day involving one or more of the following activities, and excluding activities covered by Council Directive 91/271/EEC ( 23 ):
(i)
biological treatment, such as anaerobic digestion or co-digestion;
(ii)
physico-chemical treatment;
(iii)
pre-treatment of waste for incineration or co-incineration;
(iv)
treatment of slags and ashes;
(v)
treatment in shredders of metal waste, including waste electrical and electronic equipment and end-of-life vehicles and their components.
(b)
Recovery, or a mix of recovery and disposal, of non-hazardous waste with a capacity exceeding 75 tonnes per day involving one or more of the following activities, and excluding activities covered by Directive 91/271/EEC:
(i)
biological treatment, such as anaerobic digestion;
(ii)
pre-treatment of waste for incineration or co-incineration;
(iii)
treatment of slags and ashes;
(iv)
treatment in shredders of metal waste, including waste electrical and electronic equipment and end-of-life vehicles and their components. When the only waste treatment activity carried out is anaerobic digestion, the capacity threshold for this activity shall be 100 tonnes per day. |
|
5.4. |
Landfills, as defined in Article 2(g) of Council Directive 1999/31/EC of 26 April 1999 on the landfill of waste ( 24 ), receiving more than 10 tonnes of waste per day or with a total capacity exceeding 25 000 tonnes, excluding landfills of inert waste |
|
5.5. |
Temporary storage of hazardous waste not covered under point 5.4 pending any of the activities listed in points 5.1, 5.2, 5.4 and 5.6 with a total capacity exceeding 50 tonnes, excluding temporary storage, pending collection, on the site where the waste is generated |
|
5.6. |
Underground storage of hazardous waste with a total capacity exceeding 50 tonnes |
6. Other activities
|
6.1. |
Production in industrial installations of:
(a)
pulp from timber or other fibrous materials;
(b)
paper or card board with a production capacity exceeding 20 tonnes per day;
(c)
one or more of the following wood-based panels: oriented strand board, particleboard or fibreboard with a production capacity exceeding 600 m3 per day. |
|
6.2. |
Pre-treatment (operations such as washing, bleaching, mercerisation), dyeing or finishing of textile fibres or textiles where the treatment capacity exceeds 10 tonnes per day. |
|
6.3. |
Tanning of hides and skins where the treatment capacity exceeds 12 tonnes of finished products per day |
|
6.4. |
(a)
Operating slaughterhouses with a carcass production capacity greater than 50 tonnes per day
(b)
Treatment and processing, other than exclusively packaging, of the following raw materials, whether previously processed or unprocessed, intended for the production of food or feed from:
(i)
only animal raw materials (other than exclusively milk) with a finished product production capacity greater than 75 tonnes per day;
(ii)
only vegetable raw materials with a finished product production capacity greater than 300 tonnes per day or 600 tonnes per day where the installation operates for a period of no more than 90 consecutive days in any year;
(iii)
animal and vegetable raw materials, both in combined and separate products, with a finished product production capacity in tonnes per day greater than:
—
75 if A is equal to 10 or more; or,
—
[300- (22,5 × A)] in any other case,
where ‘A’ is the portion of animal material (in percent of weight) of the finished product production capacity. Packaging shall not be included in the final weight of the product. This subsection shall not apply where the raw material is milk only.
(c)
Treatment and processing of milk only, the quantity of milk received being greater than 200 tonnes per day (average value on an annual basis). |
|
6.5. |
Disposal or recycling of animal carcasses or animal by-products with a treatment capacity exceeding 10 tonnes per day. |
|
6.6. |
Electrolysis of water for production of hydrogen where the production capacity exceeds 50 tonnes per day. |
|
6.7. |
Surface treatment of substances, objects or products using organic solvents, in particular for dressing, printing, coating, degreasing, waterproofing, sizing, painting, cleaning or impregnating, with an organic solvent consumption capacity of more than 150 kg per hour or more than 200 tonnes per year |
|
6.8. |
Production of carbon (hard-burnt coal) or electrographite by means of incineration or graphitisation |
|
6.9. |
Capture of CO2 streams from installations covered by this Directive for the purposes of geological storage pursuant to Directive 2009/31/EC |
|
6.10. |
Preservation of wood and wood products with chemicals with a production capacity exceeding 75 m3 per day other than exclusively treating against sapstain |
|
6.11. |
Independently operated treatment of waste water not covered by Directive 91/271/EEC and discharged by an installation covered by Chapter II |
ANNEX Ia
Activities referred to in Article 70a
Installations fall within the scope of this annex if they fall within one or more of the following activity categories:
Rearing of pigs representing 350 LSU or more, excluding rearing activities that are carried out under organic production regimes in accordance with Regulation (EU) 2018/848, or where the stocking density is less than 2 LSU/hectare used only for grazing or growing fodder or forage used for feeding the animals and the animals are reared outside for a significant amount of time in a year or seasonally reared outside.
Rearing of only laying hens representing 300 LSU or more, or rearing of only other poultry categories representing 280 LSU or more. In installations rearing a mix of poultry including laying hens, the threshold shall be 280 LSU and the capacity shall be calculated using 0,93 as weighting factor ( 25 ) for laying hens.
Rearing of any mix of pigs or poultry representing 380 LSU or more, excluding rearing of pigs in installations operating under organic production regimes in accordance with Regulation (EU) 2018/848, or where the stocking density is less than 2 LSU/hectare used only for grazing or growing fodder or forage used for feeding the animals and the animals are reared outside for a significant amount of time in a year or seasonally reared outside.
The LSU level of an installation is calculated using the following conversion rates:
Pigs:
Breeding sows ≥ 50 kg … 0,500
Piglets ≤ 20 kg … 0,027
Other pigs … 0,300
Poultry:
Broilers … 0,007
Laying hens … 0,014
Turkeys … 0,030
Ducks … 0,010
Geese … 0,020
Ostriches … 0,350
Other poultry fowls … 0,001
ANNEX II
Principles to be complied with when granting a derogation referred to in Article 15(5)
Derogations provided in accordance with Article 15(5) shall respect the following principles:
1. Costs
1.1. Costs referred to in Article 15(5) shall be the costs of complying with the emission levels associated with best available techniques and include both capital costs and operating costs. Wider social or economic costs shall not be included.
1.2. The evaluation of the costs shall be quantitative, and supported by a qualitative assessment.
1.3. Costs taken into account in the evaluation shall:
represent net value costs, after deduction of any financial benefits from applying best available techniques;
include the cost of accessing financial capital required to finance the best available techniques;
be calculated using a discount rate to take account of differences in monetary value over time.
1.4. The application for a derogation shall clearly identify the source of the costs and the methods used to calculate them, including the discount rate mentioned in point 1.3(c) and the estimation of uncertainties associated with the costs evaluation.
1.5. Costs evaluated by the operator shall be assessed by the competent authority, based on information from other sources such as technology providers, peer-reviewed research, expert judgements or data from other installations where best available techniques were recently installed.
2. Environmental benefits
2.1. Environmental benefits referred to in Article 15(6) shall be environmental benefits of complying with the emission levels associated with best available techniques.
2.2. The evaluation of environmental benefits shall be quantitative (in monetary terms) and supported by a qualitative assessment. Established pollutant damage costs shall be used where available.
2.3. The evaluation of environmental benefits shall consider a discount rate applied to any monetised benefits which addresses differences in value to society over time.
2.4. The application for a derogation shall clearly identify the source of the environmental benefits information and the methods used to calculate the environmental benefits, including the discount rate mentioned in point 1.3(c) and the estimate of uncertainties associated with the evaluation of the environmental benefits.
2.5. Environmental benefits evaluated by the operator shall be assessed by the competent authority, based on expert judgement or data from other installations where the best available techniques were recently installed.
3. Disproportionality of costs compared to environmental benefits
3.1. For the purpose of determining if there is a disproportionality, the costs of complying with the emission levels associated with best available techniques, and the benefits of such compliance, shall be compared.
3.2. The comparison mechanism shall include the following elements:
a method to address uncertainties in evaluating costs and environmental benefits;
a specification of the margin by which the costs should exceed the environmental benefits.
ANNEX III
Criteria for determining best available techniques
|
1. |
the use of low-waste technology; |
|
2. |
the use of less hazardous substances, including less use of substances of very high concern; |
|
3. |
the furthering of recovery and recycling of substances generated and used in the process and of waste, where appropriate; |
|
4. |
comparable processes, facilities or methods of operation which have been tried with success on an industrial scale; |
|
5. |
technological advances, including digital tools, and changes in scientific knowledge and understanding; |
|
6. |
the nature, effects and volume of the emissions concerned; |
|
7. |
the commissioning dates for new or existing installations; |
|
8. |
the length of time needed to introduce the best available technique; |
|
9. |
the consumption and nature of raw materials, including water, used in the process and resource efficiency and reuse and decarbonisation; |
|
10. |
the need to prevent or reduce to a minimum the overall impact of the emissions on the environment, including biodiversity, and the risks to it; |
|
11. |
the need to prevent accidents and to minimise the consequences for the environment and human health; |
|
12. |
information published by public international organisations. |
ANNEX IV
Public participation in decision-making
|
1. |
The public shall be informed through public notices and on a webpage of the following matters early in the procedure for the taking of a decision or, at the latest, as soon as the information can reasonably be provided:
(a)
the application for a permit or, as the case may be, the proposal for the updating of a permit or of permit conditions in accordance with Article 21, including the description of the elements listed in Article 12(1);
(b)
where applicable, the fact that a decision is subject to a national or transboundary environmental impact assessment or to consultations between Member States in accordance with Article 26;
(c)
details of the competent authorities responsible for taking the decision, those from which relevant information can be obtained, those to which comments or questions can be submitted, and details of the time schedule for transmitting comments or questions;
(d)
the nature of possible decisions or, where there is one, the draft decision;
(e)
where applicable, the details relating to a proposal for the updating of a permit or of permit conditions;
(f)
an indication of the times and places where, or means by which, the relevant information will be made available;
(g)
details of the arrangements for public participation and consultation made pursuant to point 5. |
|
2. |
Member States shall ensure that, within appropriate time-frames, the following is made available to the public concerned:
(a)
in accordance with national law, the main reports and advice issued to the competent authority or authorities at the time when the public concerned were informed in accordance with point 1;
(b)
in accordance with Directive 2003/4/EC, information other than that referred to in point 1 which is relevant for the decision in accordance with Article 5 of this Directive and which only becomes available after the time the public concerned was informed in accordance with point 1. |
|
3. |
The members of the public concerned shall be given early and effective opportunity to express comments and opinions to the competent authority before a decision is taken. |
|
4. |
The results of the consultations held pursuant to this Annex must be taken into due account in the taking of a decision. |
|
5. |
Reasonable timeframes for the different phases shall be provided, allowing sufficient time to inform the public and for the members of the public concerned to prepare and participate effectively in environmental decision-making subject to this Annex. |
ANNEX V
Technical provisions relating to combustion plants
PART 1
Emission limit values for combustion plants referred to in Article 30(2)
|
1. |
All emission limit values shall be calculated at a temperature of 273,15 K, a pressure of 101,3 kPa and after correction for the water vapour content of the waste gases and at a standardised O2 content of 6 % for solid fuels, 3 % for combustion plants, other than gas turbines and gas engines using liquid and gaseous fuels and 15 % for gas turbines and gas engines. |
|
2. |
Emission limit values (mg/Nm3) for SO2 for combustion plants using solid or liquid fuels with the exception of gas turbines and gas engines
Combustion plants, using solid fuels which were granted a permit before 27 November 2002 or the operators of which had submitted a complete application for a permit before that date, provided that the plant was put into operation no later than 27 November 2003, and which do not operate more than 1 500 operating hours per year as a rolling average over a period of 5 years, shall be subject to an emission limit value for SO2 of 800 mg/Nm3. Combustion plants using liquid fuels, which were granted a permit before 27 November 2002 or the operators of which had submitted a complete application for a permit before that date, provided that the plant was put into operation no later than 27 November 2003, and which do not operate more than 1 500 operating hours per year as a rolling average over a period of 5 years, shall be subject to an emission limit value for SO2 of 850 mg/Nm3 in case of plants with a total rated thermal input not exceeding 300 MW and of 400 mg/Nm3 in case of plants with a total rated thermal input greater than 300 MW. A part of a combustion plant discharging its waste gases through one or more separate flues within a common stack, and which does not operate more than 1 500 operating hours per year as a rolling average over a period of 5 years, may be subject to the emission limit values set out in the preceding two paragraphs in relation to the total rated thermal input of the entire combustion plant. In such cases the emissions through each of those flues shall be monitored separately. |
|
3. |
Emission limit values (mg/Nm3) for SO2 for combustion plants using gaseous fuels with the exception of gas turbines and gas engines
Combustion plants, firing low calorific gases from gasification of refinery residues, which were granted a permit before 27 November 2002 or the operators of which had submitted a complete application for a permit before that date, provided that the plant was put into operation no later than 27 November 2003, shall be subject to an emission limit value for SO2 of 800 mg/Nm3. |
|
4. |
Emission limit values (mg/Nm3) for NOx for combustion plants using solid or liquid fuels with the exception of gas turbines and gas engines
Combustion plants in chemical installations using liquid production residues as non-commercial fuel for own consumption with a total rated thermal input not exceeding 500 MW which were granted a permit before 27 November 2002 or the operators of which had submitted a complete application for a permit before that date, provided that the plant was put into operation no later than 27 November 2003, shall be subject to an emission limit value for NOx of 450 mg/Nm3. Combustion plants using solid or liquid fuels with a total rated thermal input not exceeding 500 MW which were granted a permit before 27 November 2002 or the operators of which had submitted a complete application for a permit before that date, provided that the plant was put into operation no later than 27 November 2003, and which do not operate more than 1 500 operating hours per year as a rolling average over a period of 5 years, shall be subject to an emission limit value for NOx of 450 mg/Nm3. Combustion plants using solid fuels with a total rated thermal input greater than 500 MW, which were granted a permit before 1 July 1987 and which do not operate more than 1 500 operating hours per year as a rolling average over a period of 5 years, shall be subject to an emission limit value for NOx of 450 mg/Nm3. Combustion plants using liquid fuels, with a total rated thermal input greater than 500 MW which were granted a permit before 27 November 2002 or the operators of which had submitted a complete application for a permit before that date, provided that the plant was put into operation no later than 27 November 2003, and which do not operate more than 1 500 operating hours per year as a rolling average over a period of 5 years, shall be subject to an emission limit value for NOx of 400 mg/Nm3. A part of a combustion plant discharging its waste gases through one or more separate flues within a common stack, and which does not operate more than 1 500 operating hours per year as a rolling average over a period of 5 years, may be subject to the emission limit values set out in the preceding three paragraphs in relation to the total rated thermal input of the entire combustion plant. In such cases the emissions through each of those flues shall be monitored separately. |
||||||||||||||||||||
|
5. |
Gas turbines (including combined cycle gas turbines (CCGT)) using light and middle distillates as liquid fuels shall be subject to an emission limit value for NOx of 90 mg/Nm3 and for CO of 100 mg/Nm3. Gas turbines for emergency use that operate less than 500 operating hours per year are not covered by the emission limit values set out in this point. The operator of such plants shall record the used operating hours. |
|
6. |
Emission limit values (mg/Nm3) for NOx and CO for gas fired combustion plants
For gas turbines (including CCGT), the NOx and CO emission limit values set out in the table contained in this point apply only above 70 % load. For gas turbines (including CCGT) which were granted a permit before 27 November 2002 or the operators of which had submitted a complete application for a permit before that date, provided that the plant was put into operation no later than 27 November 2003, and which do not operate more than 1 500 operating hours per year as a rolling average over a period of 5 years, the emission limit value for NOx is 150 mg/Nm3 when firing natural gas and 200 mg/Nm3 when firing other gases or liquid fuels. A part of a combustion plant discharging its waste gases through one or more separate flues within a common stack, and which does not operate more than 1 500 operating hours per year as a rolling average over a period of 5 years, may be subject to the emission limit values set out in the preceding paragraph in relation to the total rated thermal input of the entire combustion plant. In such cases the emissions through each of those flues shall be monitored separately. Gas turbines and gas engines for emergency use that operate less than 500 operating hours per year are not covered by the emission limit values set out in this point. The operator of such plants shall record the used operating hours. |
||||||||||||||||||||||||
|
7. |
Emission limit values (mg/Nm3) for dust for combustion plants using solid or liquid fuels with the exception of gas turbines and gas engines
|
||||||||||||||||||||
|
8. |
Emission limit values (mg/Nm3) for dust for combustion plants using gaseous fuels with the exception of gas turbines and gas engines
|
PART 2
Emission limit values for combustion plants referred to in Article 30(3)
|
1. |
All emission limit values shall be calculated at a temperature of 273,15 K, a pressure of 101,3 kPa and after correction for the water vapour content of the waste gases and at a standardised O2 content of 6 % for solid fuels, 3 % for combustion plants other than gas turbines and gas engines using liquid and gaseous fuels and 15 % for gas turbines and gas engines. In case of combined cycle gas turbines with supplementary firing, the standardised O2 content may be defined by the competent authority, taking into account the specific characteristics of the installation concerned. |
|
2. |
Emission limit values (mg/Nm3) for SO2 for combustion plants using solid or liquid fuels with the exception of gas turbines and gas engines
|
|
3. |
Emission limit values (mg/Nm3) for SO2 for combustion plants using gaseous fuels with the exception of gas turbines and gas engines
|
|
4. |
Emission limit values (mg/Nm3) for NOx for combustion plants using solid or liquid fuels with the exception of gas turbines and gas engines
|
|
5. |
Gas turbines (including CCGT) using light and middle distillates as liquid fuels shall be subject to an emission limit value for NOx of 50 mg/Nm3 and for CO of 100 mg/Nm3 Gas turbines for emergency use that operate less than 500 operating hours per year are not covered by the emission limit values set out in this point. The operator of such plants shall record the used operating hours. |
|
6. |
Emission limit values (mg/Nm3) for NOx and CO for gas fired combustion plants
For gas turbines (including CCGT), the NOx and CO emission limit values set out in this point apply only above 70 % load. Gas turbines and gas engines for emergency use that operate less than 500 operating hours per year are not covered by the emission limit values set out in this point. The operator of such plants shall record the used operating hours. |
|||||||||||||||
|
7. |
Emission limit values (mg/Nm3) for dust for combustion plants using solid or liquid fuels with the exception of gas turbines and gas engines
|
|
8. |
Emission limit values (mg/Nm3) for dust for combustion plants using gaseous fuels with the exception of gas turbines and gas engines
|
PART 3
Emission monitoring
|
1. |
The concentrations of SO2, NOx and dust in waste gases from each combustion plant with a total rated thermal input of 100 MW or more shall be measured continuously. The concentration of CO in waste gases from each combustion plant firing gaseous fuels with a total rated thermal input of 100 MW or more shall be measured continuously. |
|
2. |
The competent authority may decide not to require the continuous measurements referred to in point 1 in the following cases:
(a)
for combustion plants with a life span of less than 10 000 operational hours;
(b)
for SO2 and dust from combustion plants firing natural gas;
(c)
for SO2 from combustion plants firing oil with known sulphur content in cases where there is no waste gas desulphurisation equipment;
(d)
for SO2 from combustion plants firing biomass if the operator can prove that the SO2 emissions can under no circumstances be higher than the prescribed emission limit values. |
|
3. |
Where continuous measurements are not required, measurements of SO2, NOx, dust and, for gas fired plants, also of CO shall be required at least once every 6 months. |
|
4. |
For combustion plants firing coal or lignite, the emissions of total mercury shall be measured at least once per year. |
|
5. |
As an alternative to the measurements of SO2 and NOx referred to in point 3, other procedures, verified and approved by the competent authority, may be used to determine the SO2 and NOx emissions. Such procedures shall use relevant CEN standards or, if CEN standards are not available, ISO, national or other international standards which ensure the provision of data of an equivalent scientific quality. |
|
6. |
The competent authority shall be informed of significant changes in the type of fuel used or in the mode of operation of the plant. The competent authority shall decide whether the monitoring requirements laid down in points 1 to 4 are still adequate or require adaptation. |
|
7. |
The continuous measurements carried out in accordance with point 1 shall include the measurement of the oxygen content, temperature, pressure and water vapour content of the waste gases. The continuous measurement of the water vapour content of the waste gases shall not be necessary, provided that the sampled waste gas is dried before the emissions are analysed. |
|
8. |
Sampling and analysis of relevant polluting substances and measurements of process parameters as well as the quality assurance of automated measuring systems and the reference measurement methods to calibrate those systems shall be carried out in accordance with CEN standards. If CEN standards are not available, ISO, national or other international standards which ensure the provision of data of an equivalent scientific quality shall apply. The automated measuring systems shall be subject to control by means of parallel measurements with the reference methods at least once per year. The operator shall inform the competent authority about the results of the checking of the automated measuring systems without undue delay. |
|
9. |
At the emission limit value level, the values of the 95 % confidence intervals of a single measured result shall not exceed the following percentages of the emission limit values:
|
|
10. |
The validated hourly and daily average values shall be determined from the measured valid hourly average values after having subtracted the value of the confidence interval specified in point 9. Any day in which more than three hourly average values are invalid due to a malfunction or the maintenance of the automated measuring system shall be invalidated. If more than 10 days in a year are invalidated for such situations, the competent authority shall require the operator to take adequate measures to improve the reliability of the automated measuring system without undue delay. |
|
11. |
In the case of plants which must comply with the rates of desulphurisation referred to in Article 31, the sulphur content of the fuel which is fired in the combustion plant shall also be regularly monitored. The competent authorities shall be informed of substantial changes in the type of fuel used. |
PART 4
Assessment of compliance with emission limit values
|
1. |
In the case of continuous measurements, the emission limit values set out in Parts 1 and 2 shall be regarded as having been complied with if the evaluation of the measurement results indicates, for operating hours within a calendar year, that all of the following conditions have been met:
(a)
no validated monthly average value exceeds the relevant emission limit values set out in Parts 1 and 2;
(b)
no validated daily average value exceeds 110 % of the relevant emission limit values set out in Parts 1 and 2;
(c)
in cases of combustion plants composed only of boilers using coal with a total rated thermal input below 50 MW, no validated daily average value exceeds 150 % of the relevant emission limit values set out in Parts 1 and 2,
(d)
95 % of all the validated hourly average values over the year do not exceed 200 % of the relevant emission limit values set out in Parts 1 and 2. The validated average values are determined as set out in point 10 of Part 3. For the purpose of the calculation of the average emission values, the values measured during the periods referred to in Article 30(5) and (6) and Article 37 as well as during the start-up and shut-down periods shall be disregarded. |
|
2. |
Where continuous measurements are not required, the emission limit values set out in Parts 1 and 2 shall be regarded as having been complied with if the results of each of the series of measurements or of the other procedures defined and determined according to the rules laid down by the competent authorities do not exceed the emission limit values. |
PART 5
Minimum rate of desulphurisation
|
1. |
Minimum rate of desulphurisation for combustion plants referred to in Article 30(2)
|
|||||||||||||||||
|
2. |
Minimum rate of desulphurisation for combustion plants referred to in Article 30(3)
|
PART 6
Compliance with rate of desulphurisation
The minimum rates of desulphurisation set out in Part 5 of this Annex shall apply as a monthly average limit value.
PART 7
Average emission limit values for multi-fuel firing combustion plants within a refinery
Average emission limit values (mg/Nm3) for SO2 for multi-fuel firing combustion plants within a refinery, with the exception of gas turbines and gas engines, which use the distillation and conversion residues from the refining of crude-oil for own consumption, alone or with other fuels:
for combustion plants which were granted a permit before 27 November 2002 or the operators of which had submitted a complete application for a permit before that date, provided that the plant was put into operation no later than 27 November 2003: 1 000 mg/Nm3;
for other combustion plants: 600 mg/Nm3.
These emission limit values shall be calculated at a temperature of 273,15 K, a pressure of 101,3 kPa and after correction for the water vapour content of the waste gases and at a standardised O2 content of 6 % for solid fuels and 3 % for liquid and gaseous fuels.
ANNEX VI
Technical provisions relating to waste incineration plants and waste co-incineration plants
PART 1
Definitions
For the purpose of this Annex the following definitions shall apply:
‘existing waste incineration plant’ means one of the following waste incineration plants:
which was in operation and had a permit in accordance with applicable Union law before 28 December 2002,
which was authorised or registered for waste incineration and had a permit granted before 28 December 2002 in accordance with applicable Union law, provided that the plant was put into operation no later than 28 December 2003,
which, in the view of the competent authority, was the subject of a full request for authorisation before 28 December 2002, provided that the plant was put into operation not later than 28 December 2004;
‘new waste incineration plant’ means any waste incineration plant not covered by point (a).
PART 2
Equivalence factors for dibenzo-p-dioxins and dibenzofurans
For the determination of the total concentration of dioxins and furans, the mass concentrations of the following dibenzo-p-dioxins and dibenzofurans shall be multiplied by the following equivalence factors before summing:
|
|
Toxic equivalence factor |
|
2,3,7,8 — Tetrachlorodibenzodioxin (TCDD) |
1 |
|
1,2,3,7,8 — Pentachlorodibenzodioxin (PeCDD) |
0,5 |
|
1,2,3,4,7,8 — Hexachlorodibenzodioxin (HxCDD) |
0,1 |
|
1,2,3,6,7,8 — Hexachlorodibenzodioxin (HxCDD) |
0,1 |
|
1,2,3,7,8,9 — Hexachlorodibenzodioxin (HxCDD) |
0,1 |
|
1,2,3,4,6,7,8 — Heptachlorodibenzodioxin (HpCDD) |
0,01 |
|
Octachlorodibenzodioxin (OCDD) |
0,001 |
|
2,3,7,8 — Tetrachlorodibenzofuran (TCDF) |
0,1 |
|
2,3,4,7,8 — Pentachlorodibenzofuran (PeCDF) |
0,5 |
|
1,2,3,7,8 — Pentachlorodibenzofuran (PeCDF) |
0,05 |
|
1,2,3,4,7,8 — Hexachlorodibenzofuran (HxCDF) |
0,1 |
|
1,2,3,6,7,8 — Hexachlorodibenzofuran (HxCDF) |
0,1 |
|
1,2,3,7,8,9 — Hexachlorodibenzofuran (HxCDF) |
0,1 |
|
2,3,4,6,7,8 — Hexachlorodibenzofuran (HxCDF) |
0,1 |
|
1,2,3,4,6,7,8 — Heptachlorodibenzofuran (HpCDF) |
0,01 |
|
1,2,3,4,7,8,9 — Heptachlorodibenzofuran (HpCDF) |
0,01 |
|
Octachlorodibenzofuran (OCDF) |
0,001 |
PART 3
Air emission limit values for waste incineration plants
|
1. |
All emission limit values shall be calculated at a temperature of 273,15 K, a pressure of 101,3 kPa and after correcting for the water vapour content of the waste gases. They are standardised at 11 % oxygen in waste gas except in case of incineration of mineral waste oil as defined in point 3 of Article 3 of Directive 2008/98/EC, when they are standardised at 3 % oxygen, and in the cases referred to in Point 2.7 of Part 6.
|
|
2. |
Emission limit values applicable in the circumstances described in Article 46(6) and Article 47. The total dust concentration in the emissions into the air of a waste incineration plant shall under no circumstances exceed 150 mg/Nm3 expressed as a half-hourly average. The air emission limit values for TOC and CO set out in points 1.2 and 1.5(b) shall not be exceeded. |
|
3. |
Member States may lay down rules governing the exemptions provided for in this Part. |
PART 4
Determination of air emission limit values for the co-incineration of waste
|
1. |
The following formula (mixing rule) shall be applied whenever a specific total emission limit value ‘C’ has not been set out in a table in this Part. The emission limit value for each relevant polluting substance and CO in the waste gas resulting from the co-incineration of waste shall be calculated as follows:
Member States may lay down rules governing the exemptions provided for in this Part. |
|
2. |
Special provisions for cement kilns co-incinerating waste
|
||||||||||||||||||||||||||||||||||
|
3. |
Special provisions for combustion plants co-incinerating waste
|
|
4. |
Special provisions for waste co-incineration plants in industrial sectors not covered under Points 2 and 3 of this Part
|
PART 5
Emission limit values for discharges of waste water from the cleaning of waste gases
|
Polluting substances |
Emission limit values for unfiltered samples (mg/l except for dioxins and furans) |
|
|
1. Total suspended solids as defined in Annex I of Directive 91/271/EEC |
(95 %) |
(100 %) |
|
30 |
45 |
|
|
2. Mercury and its compounds, expressed as mercury (Hg) |
0,03 |
|
|
3. Cadmium and its compounds, expressed as cadmium (Cd) |
0,05 |
|
|
4. Thallium and its compounds, expressed as thallium (Tl) |
0,05 |
|
|
5. Arsenic and its compounds, expressed as arsenic (As) |
0,15 |
|
|
6. Lead and its compounds, expressed as lead (Pb) |
0,2 |
|
|
7. Chromium and its compounds, expressed as chromium (Cr) |
0,5 |
|
|
8. Copper and its compounds, expressed as copper (Cu) |
0,5 |
|
|
9. Nickel and its compounds, expressed as nickel (Ni) |
0,5 |
|
|
10. Zinc and its compounds, expressed as zinc (Zn) |
1,5 |
|
|
11. Dioxins and furans |
0,3 ng/l |
|
PART 6
Monitoring of emissions
1. Measurement techniques
|
1.1. |
Measurements for the determination of concentrations of air and water polluting substances shall be carried out representatively. |
|
1.2. |
Sampling and analysis of all polluting substances including dioxins and furans, as well as the quality assurance of automated measuring systems and the reference measurement methods to calibrate them, shall be carried out in accordance with CEN-standards. If CEN standards are not available, ISO, national or other international standards which ensure the provision of data of an equivalent scientific quality shall apply. This applies also to the quality assurance system of the laboratory performing the sampling and analysis. Automated measuring systems shall be subject to control by means of parallel measurements with the reference methods at least once per year. |
|
1.3. |
At the daily emission limit value level, the values of the 95 % confidence intervals of a single measured result shall not exceed the following percentages of the emission limit values:
Periodic measurements of the emissions into air and water shall be carried out in accordance with points 1.1 and 1.2. |
2. Measurements relating to air polluting substances
|
2.1. |
The following measurements relating to air polluting substances shall be carried out:
(a)
continuous measurements of the following substances: NOx, provided that emission limit values are set, CO, total dust, TOC, HCl, HF, SO2;
(b)
continuous measurements of the following process operation parameters: temperature near the inner wall or at another representative point of the combustion chamber as authorised by the competent authority, concentration of oxygen, pressure, temperature and water vapour content of the waste gas;
(c)
at least two measurements per year of heavy metals and dioxins and furans; one measurement at least every 3 months shall, however, be carried out for the first 12 months of operation. |
|
2.2. |
The residence time as well as the minimum temperature and the oxygen content of the waste gases shall be subject to appropriate verification, at least once when the waste incineration plant or waste co-incineration plant is brought into service and under the most unfavourable operating conditions anticipated. |
|
2.3. |
The continuous measurement of HF may be omitted if treatment stages for HCl are used which ensure that the emission limit value for HCl is not being exceeded. In that case the emissions of HF shall be subject to periodic measurements as laid down in point 2.1(c). |
|
2.4. |
The continuous measurement of the water vapour content shall not be required if the sampled waste gas is dried before the emissions are analysed. |
|
2.5. |
The competent authority may decide not to require continuous measurements for HCl, HF and SO2 in waste incineration plants or waste co-incineration plants and require periodic measurements as set out in point 2.1(c) or no measurements if the operator can prove that the emissions of those pollutants can under no circumstances be higher than the prescribed emission limit values. The competent authority may decide not to require continuous measurements for NOx and require periodic measurements as set out in point 2.1(c) in existing waste incineration plants with a nominal capacity of less than 6 tonnes per hour or in existing waste co-incineration plants with a nominal capacity of less than 6 tonnes per hour if the operator can prove on the basis of information on the quality of the waste concerned, the technologies used and the results of the monitoring of emissions, that the emissions of NOx can under no circumstances be higher than the prescribed emission limit value. |
|
2.6. |
The competent authority may decide to require one measurement every 2 years for heavy metals and one measurement per year for dioxins and furans in the following cases:
(a)
the emissions resulting from co-incineration or incineration of waste are under all circumstances below 50 % of the emission limit values;
(b)
the waste to be co-incinerated or incinerated consists only of certain sorted combustible fractions of non-hazardous waste not suitable for recycling and presenting certain characteristics, and which is further specified on the basis of the assessment referred to in point (c);
(c)
the operator can prove on the basis of information on the quality of the waste concerned and the monitoring of the emissions that the emissions are under all circumstances significantly below the emission limit values for heavy metals and dioxins and furans. |
|
2.7. |
The results of the measurements shall be standardised using the standard oxygen concentrations mentioned in Part 3 or calculated according to Part 4 and by applying the formula given in Part 7. When waste is incinerated or co-incinerated in an oxygen-enriched atmosphere, the results of the measurements can be standardised at an oxygen content laid down by the competent authority reflecting the special circumstances of the individual case. When the emissions of polluting substances are reduced by waste gas treatment in a waste incineration plant or waste co-incineration plant treating hazardous waste, the standardisation with respect to the oxygen contents provided for in the first subparagraph shall be done only if the oxygen content measured over the same period as for the polluting substance concerned exceeds the relevant standard oxygen content. |
3. Measurements relating to water polluting substances
|
3.1. |
The following measurements shall be carried out at the point of waste water discharge:
(a)
continuous measurements of pH, temperature and flow;
(b)
spot sample daily measurements of total suspended solids or measurements of a flow proportional representative sample over a period of 24 hours;
(c)
at least monthly measurements of a flow proportional representative sample of the discharge over a period of 24 hours of Hg, Cd, TI, As, Pb, Cr, Cu, Ni and Zn;
(d)
at least every 6 months measurements of dioxins and furans; however, one measurement at least every 3 months shall be carried out for the first 12 months of operation. |
|
3.2. |
Where the waste water from the cleaning of waste gases is treated on site collectively with other on-site sources of waste water, the operator shall take the measurements:
(a)
on the waste water stream from the waste gas cleaning processes prior to its input into the collective waste water treatment plant;
(b)
on the other waste water stream or streams prior to its or their input into the collective waste water treatment plant;
(c)
at the point of final waste water discharge, after the treatment, from the waste incineration plant or waste co-incineration plant. |
PART 7
Formula to calculate the emission concentration at the standard percentage oxygen concentration
|
ES |
= |
calculated emission concentration at the standard percentage oxygen concentration |
|
EM |
= |
measured emission concentration |
|
OS |
= |
standard oxygen concentration |
|
OM |
= |
measured oxygen concentration |
PART 8
Assessment of compliance with emission limit values
1. Air emission limit values
|
1.1. |
The emission limit values for air shall be regarded as being complied with if:
(a)
none of the daily average values exceeds any of the emission limit values set out in point 1.1 of Part 3 or in Part 4 or calculated in accordance with Part 4;
(b)
either none of the half-hourly average values exceeds any of the emission limit values set out in column A of the table under point 1.2 of Part 3 or, where relevant, 97 % of the half-hourly average values over the year do not exceed any of the emission limit values set out in column B of the table under point 1.2 of Part 3;
(c)
none of the average values over the sampling period set out for heavy metals and dioxins and furans exceeds the emission limit values set out in points 1.3 and 1.4 of Part 3 or in Part 4 or calculated in accordance with Part 4;
(d)
for carbon monoxide (CO):
(i)
in case of waste incineration plants:
—
at least 97 % of the daily average values over the year do not exceed the emission limit value set out in point 1.5(a) of Part 3; and,
—
at least 95 % of all 10-minute average values taken in any 24-hour period or all of the half-hourly average values taken in the same period do not exceed the emission limit values set out in points 1.5(b) and (c) of Part 3; in case of waste incineration plants in which the gas resulting from the incineration process is raised to a temperature of at least 1 100 °C for at least two seconds, Member States may apply an evaluation period of 7 days for the 10-minute average values;
(ii)
in case of waste co-incineration plants: the provisions of Part 4 are met. |
|
1.2. |
The half-hourly average values and the 10-minute averages shall be determined within the effective operating time (excluding the start-up and shut-down periods if no waste is being incinerated) from the measured values after having subtracted the value of the confidence interval specified in point 1.3 of Part 6. The daily average values shall be determined from those validated average values. To obtain a valid daily average value no more than five half-hourly average values in any day shall be discarded due to malfunction or maintenance of the continuous measurement system. No more than ten daily average values per year shall be discarded due to malfunction or maintenance of the continuous measurement system. |
|
1.3. |
The average values over the sampling period and the average values in the case of periodical measurements of HF, HCl and SO2 shall be determined in accordance with the requirements of Articles 45(1)(e), 48(3) and point 1 of Part 6. |
2. Water emission limit values
The emission limit values for water shall be regarded as being complied with if:
for total suspended solids 95 % and 100 % of the measured values do not exceed the respective emission limit values as set out in Part 5;
for heavy metals (Hg, Cd, TI, As, Pb, Cr, Cu, Ni and Zn) no more than one measurement per year exceeds the emission limit values set out in Part 5; or, if the Member State provides for more than 20 samples per year, no more than 5 % of these samples exceed the emission limit values set out in Part 5;
for dioxins and furans, the measurement results do not exceed the emission limit value set out in Part 5.
ANNEX VII
Technical provisions relating to installations and activities using organic solvents
PART 1
Activities
|
1. |
In each of the following points, the activity includes the cleaning of the equipment but not the cleaning of products unless specified otherwise. |
|
2. |
Adhesive coating Any activity in which an adhesive is applied to a surface, with the exception of adhesive coating and laminating associated with printing activities. |
|
3. |
Coating activity Any activity in which a single or multiple application of a continuous film of a coating is applied to:
(a)
either of the following vehicles:
(i)
new cars, defined as vehicles of category M1 in Directive 2007/46/EC of the European Parliament and of the Council of 5 September 2007 establishing a framework for the approval of motor vehicles and their trailers, and of systems, components and separate technical units intended for such vehicles ( 26 ) and of category N1 in so far as they are coated at the same installation as M1 vehicles;
(ii)
truck cabins, defined as the housing for the driver, and all integrated housing for the technical equipment, of vehicles of categories N2 and N3 in Directive 2007/46/EC;
(iii)
vans and trucks, defined as vehicles of categories N1, N2 and N3 in Directive 2007/46/EC, but not including truck cabins;
(iv)
buses, defined as vehicles of categories M2 and M3 in Directive 2007/46/EC;
(v)
trailers, defined in categories O1, O2, O3 and O4 in Directive 2007/46/EC;
(b)
metallic and plastic surfaces including surfaces of airplanes, ships, trains, etc.;
(c)
wooden surfaces;
(d)
textile, fabric, film and paper surfaces;
(e)
leather. Coating activities do not include the coating of substrate with metals by electrophoretic and chemical spraying techniques. If the coating activity includes a step in which the same article is printed by whatever technique used, that printing step is considered part of the coating activity. However, printing activities operated as a separate activity are not included, but may be covered by Chapter V of this Directive if the printing activity falls within the scope thereof. |
|
4. |
Coil coating Any activity where coiled steel, stainless steel, coated steel, copper alloys or aluminium strip is coated with either a film forming or laminate coating in a continuous process. |
|
5. |
Dry cleaning Any industrial or commercial activity using volatile organic compounds in an installation to clean garments, furnishing and similar consumer goods with the exception of the manual removal of stains and spots in the textile and clothing industry. |
|
6. |
Footwear manufacture Any activity of producing complete footwear or parts thereof. |
|
7. |
Manufacturing of coating mixtures, varnishes, inks and adhesives The manufacture of the above final products, and of intermediates where carried out at the same site, by mixing of pigments, resins and adhesive materials with organic solvent or other carrier, including dispersion and predispersion activities, viscosity and tint adjustments and operations for filling the final product into its container. |
|
8. |
Manufacturing of pharmaceutical products The chemical synthesis, fermentation, extraction, formulation and finishing of pharmaceutical products and, where carried out at the same site, the manufacture of intermediate products. |
|
9. |
Printing Any reproduction activity of text and/or images in which, with the use of an image carrier, ink is transferred onto whatever type of surface. It includes associated varnishing, coating and laminating techniques. However, only the following sub-processes are subject to Chapter V:
(a)
flexography – a printing activity using an image carrier of rubber or elastic photopolymers on which the printing areas are above the non-printing areas, using liquid inks which dry through evaporation;
(b)
heatset web offset – a web-fed printing activity using an image carrier in which the printing and non-printing area are in the same plane, where web-fed means that the material to be printed is fed to the machine from a reel as distinct from separate sheets. The non-printing area is treated to attract water and thus reject ink. The printing area is treated to receive and transmit ink to the surface to be printed. Evaporation takes place in an oven where hot air is used to heat the printed material;
(c)
laminating associated to a printing activity – the adhering together of two or more flexible materials to produce laminates;
(d)
publication rotogravure – a rotogravure printing activity used for printing paper for magazines, brochures, catalogues or similar products, using toluene-based inks;
(e)
rotogravure – a printing activity using a cylindrical image carrier in which the printing area is below the non-printing area, using liquid inks which dry through evaporation. The recesses are filled with ink and the surplus is cleaned off the non-printing area before the surface to be printed contacts the cylinder and lifts the ink from the recesses;
(f)
rotary screen printing – a web-fed printing activity in which the ink is passed onto the surface to be printed by forcing it through a porous image carrier, in which the printing area is open and the non-printing area is sealed off, using liquid inks which dry only through evaporation. Web-fed means that the material to be printed is fed into the machine from a reel as distinct from separate sheets;
(g)
varnishing – an activity by which a varnish or an adhesive coating for the purpose of later sealing the packaging material is applied to a flexible material. |
|
10. |
Rubber conversion Any activity of mixing, milling, blending, calendering, extrusion and vulcanisation of natural or synthetic rubber and any ancillary operations for converting natural or synthetic rubber into a finished product. |
|
11. |
Surface cleaning Any activity except dry cleaning using organic solvents to remove contamination from the surface of material including degreasing. A cleaning activity consisting of more than one step before or after any other activity shall be considered as one surface cleaning activity. This activity does not refer to the cleaning of the equipment but to the cleaning of the surface of products. |
|
12. |
Vegetable oil and animal fat extraction and vegetable oil refining activities Any activity to extract vegetable oil from seeds and other vegetable matter, the processing of dry residues to produce animal feed, the purification of fats and vegetable oils derived from seeds, vegetable matter and/or animal matter. |
|
13. |
Vehicle refinishing Any industrial or commercial coating activity and associated degreasing activities performing either of the following:
(a)
the original coating of road vehicles as defined in Directive 2007/46/EC or part of them with refinishing-type materials, where this is carried out away from the original manufacturing line;
(b)
the coating of trailers (including semi-trailers) (category O in Directive 2007/46/EC). |
|
14. |
Winding wire coating Any coating activity of metallic conductors used for winding the coils in transformers and motors, etc. |
|
15. |
Wood impregnation Any activity giving a loading of preservative in timber. |
|
16. |
Wood and plastic lamination Any activity to adhere together wood and/or plastic to produce laminated products. |
PART 2
Thresholds and emission limit values
The emission limit values in waste gases shall be calculated at a temperature of 273,15 K, and a pressure of 101,3 kPa.
|
|
Activity (solvent consumption threshold in tonnes/year) |
Threshold (solvent consumption threshold in tonnes/year) |
Emission limit values in waste gases (mg C/Nm3) |
Fugitive emission limit values (percentage of solvent input) |
Total emission limit values |
Special provisions |
||
|
New installations |
Existing installations |
New installations |
Existing installations |
|||||
|
1 |
Heatset web offset printing (> 15) |
15—25 > 25 |
100 20 |
30 (1) 30 (1) |
|
(1) Solvent residue in finished product is not to be considered as part of fugitive emissions. |
||
|
2 |
Publication rotogravure (> 25) |
|
75 |
10 |
15 |
|
|
|
|
3 |
Other rotogravure, flexography, rotary screen printing, laminating or varnishing units (> 15) rotary screen printing on textile/cardboard (> 30) |
15—25 > 25 > 30 (1) |
100 100 100 |
25 20 20 |
|
(1) Threshold for rotary screen printing on textile and on cardboard. |
||
|
4 |
Surface cleaning using compounds specified in Article 59(5). (> 1) |
1—5 > 5 |
20 (1) 20 (1) |
15 10 |
|
(1) Limit value refers to mass of compounds in mg/Nm3, and not to total carbon. |
||
|
5 |
Other surface cleaning (> 2) |
2—10 > 10 |
75 (1) 75 (1) |
20 (1) 15 (1) |
|
(1) Installations which demonstrate to the competent authority that the average organic solvent content of all cleaning material used does not exceed 30 % by weight are exempt from application of these values. |
||
|
6 |
Vehicle coating (< 15) and vehicle refinishing |
> 0,5 |
50 (1) |
25 |
|
(1) Compliance in accordance with point 2 of Part 8 shall be demonstrated based on 15 minute average measurements. |
||
|
7 |
Coil coating (> 25) |
|
50 (1) |
5 |
10 |
|
(1) For installations which use techniques which allow reuse of recovered solvents, the emission limit value shall be 150. |
|
|
8 |
Other coating, including metal, plastic, textile (5), fabric, film and paper coating (> 5) |
5—15 > 15 |
100 (1) (4) 50/75 (2) (3) (4) |
25 (4) 20 (4) |
|
|
(1) Emission limit value applies to coating application and drying processes operated under contained conditions. (2) The first emission limit value applies to drying processes, the second to coating application processes. |
|
|
|
|
|
|
|
|
(3) For textile coating installations which use techniques which allow reuse of recovered solvents, the emission limit value applied to coating application and drying processes taken together shall be 150. (4) Coating activities which cannot be carried out under contained conditions (such as shipbuilding, aircraft painting) may be exempted from these values, in accordance with Article 59(3). (5) Rotary screen printing on textile is covered by activity No 3. |
||
|
9 |
Winding wire coating (> 5) |
|
|
|
10 g/kg (1) 5 g/kg (2) |
(1) Applies for installations where average diameter of wire ≤ 0,1 mm. (2) Applies for all other installations. |
||
|
10 |
Coating of wooden surfaces (> 15) |
15—25 > 25 |
100 (1) 50/75 (2) |
25 20 |
|
(1) Emission limit value applies to coating application and drying processes operated under contained conditions. (2) The first value applies to drying processes, the second to coating application processes. |
||
|
11 |
Dry cleaning |
|
|
|
20 g/kg (1) (2) |
(1) Expressed in mass of solvent emitted per kilogram of product cleaned and dried. (2) The emission limit value in point 2 of Part 4 does not apply for this activity. |
||
|
12 |
Wood impregnation (> 25) |
|
100 (1) |
45 |
11 kg/m3 |
(1) Emission limit value does not apply for impregnation with creosote. |
||
|
13 |
Coating of leather (> 10) |
10—25 > 25 > 10 (1) |
|
|
85 g/m2 75 g/m2 150 g/m2 |
Emission limit values are expressed in grams of solvent emitted per m2 of product produced. (1) For leather coating activities in furnishing and particular leather goods used as small consumer goods like bags, belts, wallets, etc. |
||
|
14 |
Footwear manufacture (> 5) |
|
|
|
25 g per pair |
Total emission limit value is expressed in grams of solvent emitted per pair of complete footwear produced. |
||
|
15 |
Wood and plastic lamination (> 5) |
|
|
|
30 g/m2 |
|
||
|
16 |
Adhesive coating (> 5) |
5—15 > 15 |
50 (1) 50 (1) |
25 20 |
|
(1) If techniques are used which allow reuse of recovered solvent, the emission limit value in waste gases shall be 150. |
||
|
17 |
Manufacture of coating mixture, varnishes, inks and adhesives (> 100) |
100—1 000 > 1 000 |
150 150 |
5 3 |
5 % of solvent input 3 % of solvent input |
The fugitive emission limit value does not include solvent sold as part of a coatings mixture in a sealed container. |
||
|
18 |
Rubber conversion (> 15) |
|
20 (1) |
25 (2) |
25 % of solvent input |
(1) If techniques are used which allow reuse of recovered solvent, the emission limit value in waste gases shall be 150. (2) The fugitive emission limit value does not include solvent sold as part of products or mixtures in a sealed container. |
||
|
19 |
Vegetable oil and animal fat extraction and vegetable oil refining activities (> 10) |
|
|
|
Animal fat: 1,5 kg/tonne Castor: 3 kg/tonne Rape seed: 1 kg/tonne Sunflower seed: 1 kg/tonne Soya beans (normal crush): 0,8 kg/tonne Soya beans (white flakes): 1,2 kg/tonne Other seeds and other vegetable matter: 3 kg/tonne (1) 1,5 kg/tonne (2) 4 kg/tonne (3) |
(1) Total emission limit values for installations processing individual batches of seeds and other vegetable matter should be set by the competent authority on a case-by-case basis, applying the best available techniques. (2) Applies to all fractionation processes excluding de-gumming (the removal of gums from the oil). (3) Applies to de-gumming. |
||
|
20 |
Manufacturing of pharmaceutical products (> 50) |
|
20 (1) |
5 (2) |
15 (2) |
5 % of solvent input |
15 % of solvent input |
(1) If techniques are used which allow reuse of recovered solvent, the emission limit value in waste gases shall be 150. (2) The fugitive emission limit value does not include solvent sold as part of products or mixtures in a sealed container. |
PART 3
Emission limit values for installations of the vehicle coating industry
|
1. |
The total emission limit values are expressed in terms of grams of organic solvent emitted in relation to the surface area of product in square metres and in kilograms of organic solvent emitted in relation to the car body. |
|
2. |
The surface area of any product dealt with in the table under point 3 is defined as the surface area calculated from the total electrophoretic coating area, and the surface area of any parts that might be added in successive phases of the coating process which are coated with the same coatings as those used for the product in question, or the total surface area of the product coated in the installation. The surface of the electrophoretic coating area is calculated using the following formula:
This method shall also be applied for other coated parts made out of sheets. Computer aided design or other equivalent methods shall be used to calculate the surface area of the other parts added, or the total surface area coated in the installation. |
|
3. |
The total emission limit values in the table below refer to all process stages carried out at the same installation from electrophoretic coating, or any other kind of coating process, through to the final wax and polish of topcoating inclusive, as well as solvent used in cleaning of process equipment, including spray booths and other fixed equipment, both during and outside of production time.
|
||||||||||||||||||||||||||||||||||||||
|
4. |
Vehicle coating installations below the solvent consumption thresholds mentioned in the table under point 3 shall meet the requirements for the vehicle refinishing sector set out in Part 2. |
PART 4
Emission limit values relating to volatile organic compounds with specific risk phrases
|
1. |
For emissions of the volatile organic compounds referred to in Article 58 where the mass flow of the sum of the compounds causing the labelling referred to in that Article is greater than, or equal to, 10 g/h, an emission limit value of 2 mg/Nm3 shall be complied with. The emission limit value refers to the mass sum of the individual compounds. |
|
2. |
For emissions of halogenated volatile organic compounds which are assigned or need to carry the hazard statements H341 or H351, where the mass flow of the sum of the compounds causing the hazard statements H341 or H351 is greater than, or equal to, 100 g/h, an emission limit value of 20 mg/Nm3 shall be complied with. The emission limit value refers to the mass sum of the individual compounds. |
PART 5
Reduction scheme
|
1. |
The operator may use any reduction scheme, specially designed for his installation. |
|
2. |
In the case of applying coatings, varnishes, adhesives or inks, the following scheme can be used. Where the following method is inappropriate, the competent authority may allow an operator to apply any alternative scheme achieving equivalent emission reductions to those achieved if the emission limit values of Parts 2 and 3 were to be applied. The design of the scheme shall take into account the following facts:
(a)
where substitutes containing little or no solvent are still under development, a time extension shall be given to the operator to implement his emission reduction plans;
(b)
the reference point for emission reductions should correspond as closely as possible to the emissions which would have resulted had no reduction action been taken. |
|
3. |
The following scheme shall operate for installations for which a constant solid content of product can be assumed:
(a)
The annual reference emission is calculated as follows:
(i)
The total mass of solids in the quantity of coating and/or ink, varnish or adhesive consumed in a year is determined. Solids are all materials in coatings, inks, varnishes and adhesives that become solid once the water or the volatile organic compounds are evaporated.
(ii)
The annual reference emissions are calculated by multiplying the mass determined in (i) by the appropriate factor listed in the table below. Competent authorities may adjust these factors for individual installations to reflect documented increased efficiency in the use of solids.
(b)
The target emission is equal to the annual reference emission multiplied by a percentage equal to:
(i)
(the fugitive emission limit value + 15), for installations falling within item 6 and the lower threshold band of items 8 and 10 of Part 2,
(ii)
(the fugitive emission limit value + 5) for all other installations.
(c)
Compliance is achieved if the actual solvent emission determined from the solvent management plan is less than or equal to the target emission. |
PART 6
Emission monitoring
|
1. |
Channels to which abatement equipment is connected, and which at the final point of discharge emit more than an average of 10 kg/h of total organic carbon, shall be monitored continuously for compliance. |
|
2. |
In the other cases, Member States shall ensure that either continuous or periodic measurements are carried out. For periodic measurements at least three measurement values shall be obtained during each measurement exercise. |
|
3. |
Measurements are not required in the case where end-of-pipe abatement equipment is not needed to comply with this Directive. |
PART 7
Solvent management plan
1. Principles
The solvent management plan shall be used to:
verify compliance as specified in Article 62;
identify future reduction options;
enable provision of information on solvent consumption, solvent emissions and compliance with the requirements of Chapter V to the public.
2. Definitions
The following definitions provide a framework for the mass balance exercise.
Inputs of organic solvents (I):
|
I1 |
The quantity of organic solvents or their quantity in mixtures purchased which are used as input into the process in the time frame over which the mass balance is being calculated. |
|
I2 |
The quantity of organic solvents or their quantity in mixtures recovered and reused as solvent input into the process. The recycled solvent is counted every time it is used to carry out the activity. |
Outputs of organic solvents (O):
|
O1 |
Emissions in waste gases. |
|
O2 |
Organic solvents lost in water, taking into account waste water treatment when calculating O5. |
|
O3 |
The quantity of organic solvents which remains as contamination or residue in products output from the process. |
|
O4 |
Uncaptured emissions of organic solvents into air. This includes the general ventilation of rooms, where air is released to the outside environment via windows, doors, vents and similar openings. |
|
O5 |
Organic solvents and/or organic compounds lost due to chemical or physical reactions (including those which are destroyed, by incineration or other waste gas or waste water treatments, or captured, as long as they are not counted under O6, O7 or O8). |
|
O6 |
Organic solvents contained in collected waste. |
|
O7 |
Organic solvents, or organic solvents contained in mixtures, which are sold or are intended to be sold as a commercially valuable product. |
|
O8 |
Organic solvents contained in mixtures recovered for reuse but not as input into the process, as long as not counted under O7. |
|
O9 |
Organic solvents released in other ways. |
|
3. |
Use of the solvent management plan for verification of compliance. The use made of the solvent management plan shall be determined by the particular requirement which is to be verified, as follows:
(a)
verification of compliance with the reduction scheme as set out in Part 5, with a total emission limit value expressed in solvent emissions per unit product, or otherwise stated in Parts 2 and 3.
(i)
for all activities using the reduction scheme as set out in Part 5, the solvent management plan shall be drawn up annually to determine the consumption (C). The consumption shall be calculated according to the following equation: C = I1 – O8 A parallel exercise shall also be undertaken to determine solids used in coating in order to derive the annual reference emission and the target emission each year.
(ii)
for assessing compliance with a total emission limit value expressed in solvent emissions per unit product or otherwise stated in Parts 2 and 3, the solvent management plan shall be drawn up annually to determine the emissions (E). The emissions shall be calculated according to the following equation: E = F + O1 Where F is the fugitive emission as defined in point (b)(i). The emission figure shall then be divided by the relevant product parameter.
(iii)
for assessing compliance with the requirements of point (b)(ii) of Article 59(6), the solvent management plan shall be drawn up annually to determine total emissions from all activities concerned, and that figure shall then be compared with the total emissions that would have resulted had the requirements of Parts 2, 3 and 5 been met for each activity separately.
(b)
Determination of fugitive emissions for comparison with the fugitive emission limit values in Part 2:
(i)
The fugitive emission shall be calculated according to one of the following equations; F = I1 – O1 – O5 – O6 – O7 – O8 or F = O2 + O3 + O4 + O9 F shall be determined either by direct measurement of the quantities or by an equivalent method or calculation, for instance by using the capture efficiency of the process. The fugitive emission limit value is expressed as a proportion of the input, which shall be calculated according to the following equation: I = I1 + I2
(ii)
Determination of fugitive emissions shall be done by a short but comprehensive set of measurements and needs not be done again until the equipment is modified. |
PART 8
Assessment of compliance with emission limit values in waste gases
|
1. |
In the case of continuous measurements the emission limit values shall be considered to be complied with if:
(a)
none of the arithmetic averages of all valid readings taken during any 24-hour period of operation of an installation or activity except start-up and shut-down operations and maintenance of equipment exceeds the emission limit values,
(b)
none of the hourly averages exceeds the emission limit values by more than a factor of 1,5. |
|
2. |
In the case of periodic measurements the emission limit values shall be considered to be complied with if, in one monitoring exercise:
(a)
the average of all the measurement values does not exceed the emission limit values,
(b)
none of the hourly averages exceeds the emission limit value by more than a factor of 1,5. |
|
3. |
Compliance with Part 4 shall be verified on the basis of the sum of the mass concentrations of the individual volatile organic compounds concerned. For all other cases, compliance shall be verified on the basis of the total mass of organic carbon emitted unless otherwise specified in Part 2. |
|
4. |
Gas volumes may be added to the waste gas for cooling or dilution purposes where technically justified but shall not be considered when determining the mass concentration of the pollutant in the waste gas. |
ANNEX VIII
Technical provisions relating to installations producing titanium dioxide
PART 1
Emission limit values for emissions into water
|
1. |
In case of installations using the sulphate process (as an annual average): 550 kg of sulphate per tonne of titanium dioxide produced. |
|
2. |
In case of installations using the chloride process (as an annual average):
(a)
130 kg chloride per tonne of titanium dioxide produced using neutral rutile,
(b)
228 kg chloride per tonne of titanium dioxide produced using synthetic rutile,
(c)
330 kg chloride per tonne of titanium dioxide produced using slag. Installations discharging into salt water (estuarine, coastal, open sea) may be subject to an emission limit value of 450 kg chloride per tonne of titanium dioxide produced using slag. |
|
3. |
For installations using the chloride process and using more than one type of ore, the emission limit values in point 2 shall apply in proportion to the quantity of the ores used. |
PART 2
Emission limit values into air
|
1. |
The emission limit values which are expressed as concentrations in mass per cubic meter (Nm3) shall be calculated at a temperature of 273,15 K, and a pressure of 101,3 kPa. |
|
2. |
For dust: 50 mg/Nm3 as an hourly average from major sources and 150 mg/Nm3 as an hourly average from any other source. |
|
3. |
For gaseous sulphur dioxide and trioxide discharged from digestion and calcination, including acid droplets calculated as SO2 equivalent:
(a)
6 kg per tonne of titanium dioxide produced as an annual average;
(b)
500 mg/Nm3 as an hourly average for plants for the concentration of waste acid. |
|
4. |
For chlorine in the case of installations using the chloride process:
(a)
5 mg/Nm3 as a daily average;
(b)
40 mg/Nm3 at any time. |
PART 3
Emission monitoring
The monitoring of emissions into air shall include at least the continuous monitoring of:
gaseous sulphur dioxide and trioxide discharged from digestion and calcination from plants for the concentration of waste acid in installations using the sulphate process;
chlorine from major sources within installations using the chloride process;
dust from major sources.
ANNEX IX
PART A
Repealed Directives with their successive amendments
(referred to in Article 81)
|
Council Directive 78/176/EEC (OJ L 54, 25.2.1978, p. 19). |
|
|
Council Directive 83/29/EEC (OJ L 32, 3.2.1983, p. 28). |
|
|
Council Directive 91/692/EEC (OJ L 377, 31.12.1991, p. 48). |
only Annex I, point (b) |
|
Council Directive 82/883/EEC (OJ L 378, 31.12.1982, p. 1). |
|
|
Act of Accession of 1985 |
only Annex I, point X.1(o) |
|
Act of Accession of 1994 |
only Annex I, point VIII.A.6 |
|
Council Regulation (EC) No 807/2003 (OJ L 122, 16.5.2003, p. 36). |
only Annex III, point 34 |
|
Regulation (EC) No 219/2009 of the European Parliament and of the Council (OJ L 87, 31.3.2009, p. 109). |
only Annex, point 3.1 |
|
Council Directive 92/112/EEC (OJ L 409, 31.12.1992, p. 11). |
|
|
Council Directive 1999/13/EC (OJ L 85, 29.3.1999, p. 1). |
|
|
Regulation (EC) No 1882/2003 of the European Parliament and of the Council (OJ L 284, 31.10.2003, p. 1). |
only Annex I, point 17 |
|
Directive 2004/42/EC of the European Parliament and of the Council (OJ L 143, 30.4.2004, p. 87). |
only Article 13(1) |
|
Directive 2008/112/EC of the European Parliament and of the Council (OJ L 345, 23.12.2008, p. 68). |
only Article 3 |
|
Directive 2000/76/EC of the European Parliament and of the Council (OJ L 332, 28.12.2000, p. 91). |
|
|
Regulation (EC) No 1137/2008 of the European Parliament and of the Council (OJ L 311, 21.11.2008, p. 1). |
only Annex, point 4.8 |
|
Directive 2001/80/EC of the European Parliament and of the Council (OJ L 309, 27.11.2001, p. 1). |
|
|
Council Directive 2006/105/EC (OJ L 363, 20.12.2006, p. 368). |
only Annex, part B, point 2 |
|
Directive 2009/31/EC of the European Parliament and of the Council (OJ L 140, 5.6.2009, p. 114). |
only Article 33 |
|
Directive 2008/1/EC of the European Parliament and of the Council (OJ L 24, 29.1.2008, p. 8). |
|
|
Directive 2009/31/EC of the European Parliament and of the Council (OJ L 140, 5.6.2009, p. 114). |
only Article 37 |
PART B
List of time-limits for transposition into national law and application
(referred to in Article 81)
|
Directive |
Time-limit for transposition |
Time-limit for application |
|
78/176/EEC |
25 February 1979 |
|
|
82/883/EEC |
31 December 1984 |
|
|
92/112/EEC |
15 June 1993 |
|
|
1999/13/EC |
1 April 2001 |
|
|
2000/76/EC |
28 December 2000 |
28 December 2002 28 December 2005 |
|
2001/80/EC |
27 November 2002 |
27 November 2004 |
|
2003/35/EC |
25 June 2005 |
|
|
2003/87/EC |
31 December 2003 |
|
|
2008/1/EC |
30 October 1999 (1) |
30 October 1999 30 October 2007 |
|
(1)
Directive 2008/1/EC is a codified version of Council Directive 96/61/EC of24 September 1996 concerning integrated pollution prevention and control (OJ L 257, 10.10.1996, p. 26) and the time-limits for transposition and application remain in force. |
||
ANNEX X
Correlation Table
|
Directive 78/176/EEC |
Directive 82/883/EEC |
Directive 92/112/EEC |
Directive 2008/1/EC |
Directive 1999/13/EC |
Directive 2000/76/EC |
Directive 2001/80/EC |
This Directive |
|
Article 1(1) |
Article 1 |
Article 1 |
|
|
|
|
Article 66 |
|
— |
— |
— |
— |
— |
— |
— |
Article 2 |
|
Article 1(2), point (a) |
|
|
Article 2(2) |
|
|
|
Article 3(2) |
|
Article 1(2), point (b) |
|
|
|
|
Article 3(1) |
|
Article 3(37) |
|
Article 1(2), points (c), (d) and (e) |
|
|
|
|
|
|
— |
|
— |
— |
— |
— |
— |
— |
— |
Article 66 |
|
Article 2 |
|
|
|
|
|
|
Article 67 |
|
Article 3 |
|
|
|
|
|
|
Article 11, points (d) and (e) |
|
Article 4 |
|
|
Article 4 |
Article 3, introductory wording and (1) |
Article 4(1) |
|
Article 4(1), first subparagraph |
|
Article 5 |
|
|
|
|
|
|
Article 11, points (d) and (e) |
|
Article 6 |
|
|
|
|
|
|
Article 11, points (d) and (e) |
|
Article 7(1) |
|
Article 10 |
|
|
|
|
Article 70(1) and 70(2), first sentence |
|
Article 7(2) and (3) |
|
|
|
|
|
|
— |
|
— |
— |
— |
— |
— |
— |
— |
Article 70(2), second sentence and 70(3) |
|
Article 8(1) |
|
|
|
|
|
|
— |
|
Article 8(2) |
|
|
|
|
|
|
Article 26(1), second subparagraph |
|
Article 9 |
|
|
|
|
|
|
— |
|
Article 10 |
|
|
|
|
|
|
— |
|
Article 11 |
|
|
|
|
|
|
Article 12 |
|
Article 12 |
|
|
|
|
|
|
— |
|
Article 13(1) |
|
|
Article 17(1), first subparagraph and 17(3), first subparagraph, first sentence |
Article 11(1), first sentence and 11(2) |
|
|
Article 72(1), first sentence |
|
— |
— |
— |
— |
— |
— |
— |
Article 72(1), second sentence |
|
Article 13(2), (3) and (4) |
|
|
|
|
|
|
— |
|
Article 14 |
|
|
|
|
|
|
— |
|
Article 15 |
Article 14 |
Article 12 |
Article 21 |
Article 15 |
Article 21 |
Article 18(1) and (3) |
Article 80 |
|
Article 16 |
Article 15 |
Article 13 |
Article 23 |
Article 17 |
Article 23 |
Article 20 |
Article 84 |
|
Annex I |
|
|
|
|
|
|
— |
|
Annex II section A introductory wording and point 1 |
|
|
|
|
|
|
— |
|
Annex II section A point 2 |
|
|
|
|
|
|
— |
|
Annex II section B |
|
|
|
|
|
|
— |
|
|
Article 2 |
|
|
|
|
|
— |
|
|
Article 3 |
|
|
|
|
|
— |
|
|
Article 4(1) and 4(2), first subparagraph |
|
|
|
|
|
— |
|
|
Article 4(2), second subparagraph |
|
|
|
|
|
— |
|
|
Article 4(3) and (4) |
|
|
|
|
|
— |
|
|
Article 5 |
|
|
|
|
|
— |
|
|
Article 6 |
|
|
|
|
|
— |
|
|
Article 7 |
|
|
|
|
|
— |
|
|
Article 8 |
|
|
|
|
|
— |
|
|
Article 9 |
|
|
|
|
|
— |
|
|
Article 10 |
|
|
|
|
|
— |
|
|
Article 11(1) |
|
|
Article 13(1) |
Article 17(1) |
|
Article 75(1) |
|
— |
— |
— |
— |
— |
— |
— |
Article 75(2) |
|
|
Article 11(2) |
|
|
|
Article 17(2) |
|
— |
|
|
Article 11(3) |
|
|
|
|
|
— |
|
|
Article 12 |
|
|
|
|
|
— |
|
|
Article 13 |
|
|
|
|
|
— |
|
|
Annex I |
|
|
|
|
|
— |
|
|
Annex II |
|
|
|
|
|
— |
|
|
Annex III |
|
|
|
|
|
— |
|
|
Annex IV |
|
|
|
|
|
— |
|
|
Annex V |
|
|
|
|
|
— |
|
|
|
Article 2(1), introductory wording |
|
|
|
|
— |
|
|
|
Article 2(1)(a), introductory wording |
|
|
|
|
— |
|
|
|
Article 2(1)(a), first indent |
|
|
|
|
Article 67, point (a) |
|
|
|
Article 2(1)(a), second indent |
|
|
|
|
Article 67, point (b) |
|
|
|
Article 2(1)(a), third indent and 2(1)(b), third indent |
|
|
|
|
Article 67, point (d) |
|
|
|
Article 2(1)(a), fourth, fifth, sixth and seventh indent |
|
|
|
|
— |
|
|
|
Article 2(1)(b), introductory wording and first, fourth, fifth, sixth and seventh indent |
|
|
|
|
— |
|
|
|
Article 2(1)(b), second indent |
|
|
|
|
Article 67, point (c) |
|
|
|
Article 2(1)(c) |
|
|
|
|
— |
|
|
|
Article 2(2) |
|
|
|
|
— |
|
|
|
Article 3 |
|
|
|
|
Article 67 |
|
|
|
Article 4 |
|
|
|
|
Article 67 |
|
|
|
Article 5 |
|
|
|
|
— |
|
|
|
Article 6, first paragraph, introductory wording |
|
|
|
|
Article 68 |
|
|
|
Article 6, first paragraph, point (a) |
|
|
|
|
Annex VIII, Part 1, point 1 |
|
|
|
Article 6, first paragraph, point (b) |
|
|
|
|
Annex VIII, Part 1, point 2 |
|
|
|
Article 6, second paragraph |
|
|
|
|
Annex VIII, Part 1, point 3 |
|
|
|
Article 7 |
|
|
|
|
— |
|
|
|
Article 8 |
|
|
|
|
— |
|
|
|
Article 9(1) introductory wording |
|
|
|
|
Article 69(2) |
|
|
|
Article 9(1)(a), introductory wording |
|
|
|
|
— |
|
|
|
Article 9(1)(a)(i) |
|
|
|
|
Annex VIII, Part 2, point 2 |
|
|
|
Article 9(1)(a)(ii) |
|
|
|
|
Annex VIII, Part 2, point 3, introductory wording, and point 3(a) |
|
|
|
Article 9(1)(a)(iii) |
|
|
|
|
Article 69(1) |
|
|
|
Article 9(1)(a)(iv) |
|
|
|
|
Annex VIII, Part 2, point 3(b) |
|
|
|
Article 9(1)(a)(v) |
|
|
|
|
— |
|
|
|
Article 9(1)(b) |
|
|
|
|
Annex VIII, Part 2, point 4 |
|
|
|
Article 9(2) and (3) |
|
|
|
|
— |
|
|
|
Article 11 |
|
|
|
|
Article 11, points (d) and (e) |
|
|
|
Annex |
|
|
|
|
— |
|
|
|
|
Article 1 |
|
|
|
Article 1 |
|
|
|
|
Article 2, introductory wording |
|
|
|
Article 3, introductory wording |
|
|
|
|
Article 2(1) |
Article 2(14) |
|
|
Article 3(1) |
|
|
|
|
Article 2(3) |
Article 2(1) |
|
|
Article 3(3) |
|
|
|
|
Article 2(4) |
|
|
|
— |
|
|
|
|
Article 2(5) |
Article 2(9) |
Article 3(8) |
Article 2(1) |
Article 3(4) |
|
|
|
|
Article 2(6), first sentence |
Article 2(13) |
Article 3(9) |
Article 2(3), first part |
Article 3(5) |
|
|
|
|
Article 2(6), second sentence |
|
|
|
Article 15(1) |
|
|
|
|
Article 2(7) |
|
|
|
Article 3(6) |
|
|
|
|
Article 2(8) |
Article 2(5) |
|
|
Article 71 |
|
|
|
|
Article 2(9), first sentence |
Article 2(7) |
Article 3(12) |
|
Article 3(7) |
|
|
|
|
Article 2(9), second sentence |
|
|
|
Article 4(2), first subparagraph |
|
— |
— |
— |
— |
— |
— |
— |
Article 4(2), second subparagraph |
|
— |
— |
— |
— |
— |
— |
— |
Article 4(3) |
|
|
|
|
Article 2(10) |
|
|
|
— |
|
— |
— |
— |
— |
— |
— |
— |
Article 3(8) |
|
|
|
|
Article 2(11), first sentence |
|
|
|
Article 3(9) |
|
|
|
|
Article 2(11), second sentence |
|
|
|
Article 20(3) |
|
|
|
|
Article 2(12), first subparagraph and Annex IV, introductory wording |
|
|
|
Article 3(10) |
|
|
|
|
Article 2(12), second subparagraph |
|
|
|
Articles 14(5), point (a) and 14(6) |
|
|
|
|
Article 2(13) |
Article 2(6) |
Article 3(11) |
Article 2(5) |
Article 3(15) |
|
|
|
|
Article 2(14) |
|
|
|
Article 3(16) |
|
|
|
|
Article 2(15) |
|
|
|
Article 3(17) |
|
— |
— |
— |
— |
— |
— |
— |
Article 3(11) to (14), (18) to (23), (26) to (30) and (34) to (36) |
|
|
|
|
Article 3(1), introductory wording |
|
|
|
Article 11, introductory wording |
|
|
|
|
Article 3(1), point (a) |
|
|
|
Article 11, points (a) and (b) |
|
|
|
|
Article 3(1), point (b) |
|
|
|
Article 11, point (c) |
|
|
|
|
Article 3(1), point (c) |
|
|
|
Article 11, points (d) and (e) |
|
|
|
|
Article 3(1), point (d) |
|
|
|
Article 11, point (f) |
|
|
|
|
Article 3(1), point (e) |
|
|
|
Article 11, point (g) |
|
|
|
|
Article 3(1), point (f) |
|
|
|
Article 11, point (h) |
|
|
|
|
Article 3(2) |
|
|
|
— |
|
|
|
|
Article 5(1) |
|
|
|
— |
|
|
|
|
Article 5(2) |
|
|
|
Article 80(1), second subparagraph |
|
|
|
|
Article 6(1), introductory wording |
|
|
|
Article 12(1), first subparagraph, introductory wording |
|
|
|
|
Article 6(1), first subparagraph, points (a) to (d) |
|
|
|
Article 12(1), first subparagraph, points (a) to (d) |
|
— |
— |
— |
— |
— |
— |
— |
Article 12(1), first subparagraph, point (e) |
|
|
|
|
Article 6(1), first subparagraph, point (e) |
|
|
|
Article 12(1), first subparagraph, point (f) |
|
|
|
|
Article 6(1), first subparagraph, point (f) |
|
|
|
Article 12(1), first subparagraph, point (g) |
|
|
|
|
Article 6(1), first subparagraph, point (g) |
|
|
|
Article 12(1), first subparagraph, point (h) |
|
|
|
|
Article 6(1), first subparagraph, point (h) |
|
|
|
Article 12(1), first subparagraph, point (i) |
|
|
|
|
Article 6(1), first subparagraph, point (i) |
|
|
|
Article 12(1), first subparagraph, point (j) |
|
|
|
|
Article 6(1), first subparagraph, point (j) |
|
|
|
Article 12(1), first subparagraph, point (k) |
|
|
|
|
Article 6(1), second subparagraph |
|
|
|
Article 12(1), second subparagraph |
|
|
|
|
Article 6(2) |
|
|
|
Article 12(2) |
|
|
|
|
Article 7 |
|
|
|
Article 5(2) |
|
|
|
|
Article 8, first paragraph |
|
Article 4(3) |
|
Article 5(1) |
|
|
|
|
Article 8, second paragraph |
|
|
|
— |
|
|
|
|
Article 9(1), first part of sentence |
|
|
|
Article 14(1), first subparagraph |
|
|
|
|
Article 9(1), second part of sentence |
|
|
|
— |
|
|
|
|
Article 9(2) |
|
|
|
Article 5(3) |
|
|
|
|
Article 9(3), first subparagraph, first and second sentence |
|
|
|
Article 14(1), second subparagraph, introductory wording and points (a) and (b) |
|
|
|
|
Article 9(3), first subparagraph, third sentence |
|
|
|
Article 14(2) |
|
— |
— |
— |
— |
— |
— |
— |
Article 14(3), (4), and (7) |
|
— |
— |
— |
— |
— |
— |
— |
Article 14(5), introductory wording and point (b) of first subparagraph and Article 14(5), second subparagraph |
|
|
|
|
Article 9(3), second subparagraph |
|
|
|
— |
|
|
|
|
Article 9(3), third subparagraph |
|
|
|
Article 9(1) |
|
|
|
|
Article 9(3), fourth subparagraph |
|
|
|
Article 9(2) |
|
|
|
|
Article 9(3), fifth subparagraph |
|
|
|
Article 9(3) |
|
|
|
|
Article 9(3), sixth subparagraph |
|
|
|
Article 9(4) |
|
— |
— |
— |
— |
— |
— |
— |
Article 10 |
|
|
|
|
Article 9(4), first part of first sentence |
|
|
|
Article 15(2) |
|
|
|
|
Article 9(4), second part of first sentence |
|
|
|
Article 15(4), first subparagraph |
|
— |
— |
— |
— |
— |
— |
— |
Article 15(4), second to fifth subparagraphs and Article 15(5) |
|
|
|
|
Article 9(4), second sentence |
|
|
|
Article 14(1), second subparagraph, point (g) |
|
— |
— |
— |
— |
— |
— |
— |
Article 14(1), second subparagraph, point (h) |
|
— |
— |
— |
— |
— |
— |
— |
Article 15(3) |
|
— |
— |
— |
— |
— |
— |
— |
Article 16 |
|
|
|
|
Article 9(5), first subparagraph |
|
|
|
Article 14(1), second subparagraph, point (c)(i) |
|
— |
— |
— |
— |
— |
— |
— |
Article 14(1), second subparagraph, point (c)(ii) |
|
— |
— |
— |
— |
— |
— |
— |
Article 14(1), second subparagraph, point (d) |
|
|
|
|
Article 9(5), second subparagraph |
|
|
|
— |
|
— |
— |
— |
— |
— |
— |
— |
Article 14(1), second subparagraph, point (e) |
|
|
|
|
Article 9(6), first subparagraph |
|
|
|
Article 14(1), second subparagraph, point (f) |
|
|
|
|
Article 9(6), second subparagraph |
|
|
|
— |
|
|
|
|
Article 9(7) |
|
|
|
— |
|
|
|
|
Article 9(8) |
|
|
|
Article 6 and Article 17(1) |
|
— |
— |
— |
— |
— |
— |
— |
Article 17(2), (3) and (4) |
|
|
|
|
Article 10 |
|
|
|
Article 18 |
|
|
|
|
Article 11 |
|
|
|
Article 19 |
|
|
|
|
Article 12(1) |
|
|
|
Article 20(1) |
|
|
|
|
Article 12(2), first sentence |
|
|
|
Article 20(2), first subparagraph |
|
|
|
|
Article 12(2), second sentence |
|
|
|
Article 20(2), second subparagraph |
|
|
|
|
Article 12(2), third sentence |
|
|
|
— |
|
|
|
|
Article 13(1) |
|
|
|
Article 21(1) |
|
— |
— |
— |
— |
— |
— |
— |
Article 21(2), (3) and (4) |
|
|
|
|
Article 13(2), introductory wording |
|
|
|
Article 21(5), introductory wording |
|
|
|
|
Article 13(2)(a) |
|
|
|
Article 21(5), point (a) |
|
|
|
|
Article 13(2)(b) |
|
|
|
— |
|
|
|
|
Article 13(2)(c) |
|
|
|
Article 21(5), point (b) |
|
|
|
|
Article 13(2)(d) |
|
|
|
— |
|
— |
— |
— |
— |
— |
— |
— |
Article 21(5), point (c) |
|
— |
— |
— |
— |
— |
— |
— |
Article 22 |
|
— |
— |
— |
— |
— |
— |
— |
Article 23(1), first subparagraph |
|
|
|
|
Article 14, introductory wording and point (a) |
|
|
|
Article 8(1) |
|
|
|
|
Article 14, point (b) |
|
|
|
Article 7, point (a) and Article 14(1), point (d)(i) |
|
— |
— |
— |
— |
— |
— |
— |
Article 7, introductory wording and points (b) and (c) |
|
— |
— |
— |
— |
— |
— |
— |
Article 14(1), point (d)(ii) |
|
|
|
|
Article 14, point (c) |
|
|
|
Article 23(1), second subparagraph |
|
— |
— |
— |
— |
— |
— |
— |
Article 23(2) to (6) |
|
|
|
|
Article 15(1), first subparagraph, introductory wording and points (a) and (b) |
Article 12(1), first subparagraph |
|
|
Article 24(1), first subparagraph, introductory wording and points (a) and (b) |
|
|
|
|
Article 15(1), first subparagraph, point (c) |
|
|
|
Article 24(1), first subparagraph, point (c) |
|
|
|
|
Article 15(1), second subparagraph |
|
|
|
Article 24(1), second subparagraph |
|
|
|
|
Article 15(2) |
|
|
|
Article 24(3)(b) |
|
|
|
|
Article 15(3) |
|
|
|
Article 24(4) |
|
|
|
|
Article 15(4) |
|
|
|
Article 24(2), introductory wording and points (a) and (b) |
|
— |
— |
— |
— |
— |
— |
— |
Article 24(2), points (c) to (f) and Article 24(3), introductory wording and point (a) |
|
|
|
|
Article 16 |
|
|
|
Article 25 |
|
|
|
|
Article 17(1), second subparagraph |
|
|
|
— |
|
|
|
|
Article 17(2), first subparagraph |
|
|
|
Article 13(1) |
|
— |
— |
— |
— |
— |
— |
— |
Article 13(2) to (7) |
|
|
|
|
Article 17(2), second subparagraph |
|
|
|
— |
|
|
|
|
Article 17(3), first subparagraph, second and third sentence |
Article 11(1), second sentence |
|
|
Article 72(2) |
|
|
|
|
Article 17(3), first subparagraph, fourth sentence |
|
|
|
— |
|
— |
— |
— |
— |
— |
— |
— |
Article 72(3) and (4) |
|
|
|
|
Article 17(3), second subparagraph |
|
|
|
— |
|
|
|
|
Article 17(3), third subparagraph |
Article 11(3) |
|
|
Article 73(1) |
|
— |
— |
— |
— |
— |
— |
— |
Article 73(2) |
|
|
|
|
Article 17(4) |
|
|
|
— |
|
— |
— |
— |
— |
— |
— |
— |
Article 74 |
|
— |
— |
— |
— |
— |
— |
— |
Article 27 |
|
|
|
|
Article 18 |
|
|
Article 11 |
Article 26 |
|
|
|
|
Article 19 |
|
|
|
— |
|
|
|
|
Article 20 |
|
|
|
— |
|
|
|
|
Article 21 |
|
|
|
Article 80(2) |
|
|
|
|
Article 22 |
|
Article 18 |
Article 17 |
Article 81 |
|
— |
— |
— |
— |
— |
— |
— |
Article 82 |
|
|
|
|
Article 23 |
Article 16 |
Article 22 |
Article 19 |
Article 83 |
|
— |
— |
— |
— |
— |
— |
— |
Article 2(1) |
|
|
|
|
Annex I, paragraph 1 of introductory wording |
|
|
|
Article 2(2) |
|
|
|
|
Annex I, paragraph 2 of introductory wording |
|
|
|
Annex I, first subparagraph of introductory wording, first sentence |
|
— |
— |
— |
— |
— |
— |
— |
Annex I, first subparagraph of introductory wording, second sentence |
|
— |
— |
— |
— |
— |
— |
— |
Annex I, second subparagraph of introductory wording |
|
|
|
|
Annex I, points 1.1 to 1.3 |
|
|
|
Annex I, points 1.1 to 1.3 |
|
|
|
|
Annex I, point 1.4 |
|
|
|
Annex I, point 1.4(a) |
|
— |
— |
— |
— |
— |
— |
— |
Annex I, point 1.4(b) |
|
|
|
|
Annex I, point 2 |
|
|
|
Annex I, point 2 |
|
|
|
|
Annex I, point 3.1 |
|
|
|
Annex I, point 3.1(a) and (b) |
|
— |
— |
— |
— |
— |
— |
— |
Annex I, point 3.1(c) |
|
|
|
|
Annex I, points 3.2 to 3.5 |
|
|
|
Annex I, points 3.2 to 3.5 |
|
|
|
|
Annex I, point 4 |
|
|
|
Annex I, point 4 |
|
|
|
|
Annex I, point 5, introductory wording |
|
|
|
— |
|
|
|
|
Annex I, point 5.1 |
|
|
|
Annex I, points 5.1(b), (f), (g), (i), (j) and 5.2(b) |
|
— |
— |
— |
— |
— |
— |
— |
Annex I, points 5.1(a), (c), (d), (e), (h), (k) |
|
|
|
|
Annex I, point 5.2 |
|
|
|
Annex I, point 5.2(a) |
|
|
|
|
Annex I, point 5.3 |
|
|
|
Annex I, point 5.3(a)(i) and (ii) |
|
— |
— |
— |
— |
— |
— |
— |
Annex I, point 5.3(a)(iii) to (v) and 5.3(b) |
|
|
|
|
Annex I, point 5.4 |
|
|
|
Annex I, point 5.4 |
|
— |
— |
— |
— |
— |
— |
— |
Annex I, points 5.5 and 5.6 |
|
|
|
|
Annex I, points 6.1(a) and (b) |
|
|
|
Annex I, points 6.1(a) and (b) |
|
— |
— |
— |
— |
— |
— |
— |
Annex I, point 6.1(c) |
|
|
|
|
Annex I, points 6.2 – 6.4(b) |
|
|
|
Annex I, points 6.2 – 6.4(b)(ii) |
|
— |
— |
— |
— |
— |
— |
— |
Annex I, point 6.4 (b)(iii) |
|
|
|
|
Annex I, points 6.4(c) – 6.9 |
|
|
|
Annex I, points 6.4(c) – 6.9 |
|
— |
— |
— |
— |
— |
— |
— |
Annex I, points 6.10 and 6.11 |
|
|
|
|
Annex II |
|
|
|
— |
|
|
|
|
Annex III |
|
|
|
Annex II, ‘Air’, and ‘Water’, points 1 to 12 |
|
— |
— |
— |
— |
— |
— |
— |
Annex II, ‘Water’, point 13 |
|
|
|
|
Annex IV |
|
|
|
Annex III |
|
|
|
|
Annex V |
|
|
|
Annex IV |
|
|
|
|
|
Article 1 |
|
|
Article 56 |
|
|
|
|
|
Article 2(2) |
|
|
Article 57(1) |
|
|
|
|
|
Article 2(3) |
|
|
— |
|
|
|
|
|
Article 2(4) |
|
|
Article 63(1) |
|
|
|
|
|
Article 2(8) |
|
|
Article 4(1), third subparagraph |
|
|
|
|
|
Article 2(10) |
|
|
Article 57(3) |
|
|
|
|
|
Article 2(11) |
|
|
Article 57(2) |
|
|
|
|
|
Article 2(12) |
|
|
Article 57(4) |
|
|
|
|
|
Article 2(15) |
|
|
Article 57(5) |
|
|
|
|
|
Article 2(16) |
|
|
Article 3(44) |
|
|
|
|
|
Article 2(17) |
|
|
Article 3(45) |
|
|
|
|
|
Article 2(18) |
|
|
Article 3(46) |
|
|
|
|
|
Article 2(19) |
|
|
— |
|
|
|
|
|
Article 2(20) |
|
|
Article 3(47) |
|
|
|
|
|
Article 2(21) |
|
|
Article 57(6) |
|
|
|
|
|
Article 2(22) |
|
|
Article 57(7) |
|
|
|
|
|
Article 2(23) |
|
|
Article 57(8) |
|
|
|
|
|
Article 2(24) |
|
|
Article 57(9) |
|
|
|
|
|
Article 2(25) |
|
|
Article 57(10) |
|
|
|
|
|
Article 2(26) |
|
|
Article 57(11) |
|
|
|
|
|
Article 2(27) |
|
|
— |
|
|
|
|
|
Article 2(28) |
|
|
Article 63(1) |
|
|
|
|
|
Article 2(29) |
|
|
— |
|
|
|
|
|
Article 2(30) |
|
|
Article 57(12) |
|
|
|
|
|
Article 2(31) |
|
|
Annex VII, Part 2, first sentence Annex VIII, Part 2, point 1 |
|
|
|
|
|
Article 2(32) |
|
|
— |
|
|
|
|
|
Article 2(33) |
|
|
Article 57(13) |
|
|
|
|
|
Article 3(2) |
|
|
Article 4(1), second subparagraph |
|
|
|
|
|
Article 4(1), (2) and(3) |
|
|
Article 4(1), first and second subparagraph |
|
|
|
|
|
Article 4(4) |
|
|
Article 63(2) |
|
|
|
|
|
Article 5(1) |
|
|
Article 59(1), first subparagraph, introductory wording |
|
|
|
|
|
Article 5(2) |
|
|
Article 59(1) first subparagraph, points (a) and (b) |
|
|
|
|
|
Article 5(3), first subparagraph, point (a) |
|
|
Article 59(2) |
|
|
|
|
|
Article 5(3), first subparagraph, point (b) |
|
|
Article 59(3) |
|
|
|
|
|
Article 5(3), second subparagraph |
|
|
Article 59(4) |
|
— |
— |
— |
— |
— |
— |
— |
Article 59(5) |
|
|
|
|
|
Article 5(4) |
|
|
— |
|
|
|
|
|
Article 5(5) |
|
|
Article 59(6) |
|
|
|
|
|
Article 5(6) |
|
|
Article 58 |
|
|
|
|
|
Article 5(7) |
|
|
Annex VII, Part 4, point 1 |
|
|
|
|
|
Article 5(8) first subparagraph |
|
|
Annex VII, Part 4, point 2 |
|
|
|
|
|
Article 5(8) second subparagraph |
|
|
— |
|
|
|
|
|
Article 5(9) |
|
|
— |
|
|
|
|
|
Article 5(10) |
|
|
Article 59(7) |
|
|
|
|
|
Article 5(11), (12) and (13) |
|
|
— |
|
|
|
|
|
Article 6 |
|
|
— |
|
|
|
|
|
Article 7(1), introductory wording and first, second, third and fourth indent |
|
|
Article 64 |
|
|
|
|
|
Article 7(1), closing wording |
|
|
— |
|
|
|
|
|
Article 7(2) |
|
|
— |
|
|
|
|
|
Article 8(1) |
|
|
Article 14(1), point (d), Article 60 |
|
— |
— |
— |
— |
— |
— |
— |
Article 61 |
|
|
|
|
|
Article 8(2) |
|
|
Annex VII, Part 6, point 1 |
|
|
|
|
|
Article 8(3) |
|
|
Annex VII, Part 6, point 2 |
|
|
|
|
|
Article 8(4) |
|
|
Annex VII Part 6, point 3 |
|
|
|
|
|
Article 8(5) |
|
|
— |
|
|
|
|
|
Article 9(1), first subparagraph, introductory wording |
|
|
Article 62, first subparagraph, introductory wording |
|
|
|
|
|
Article 9(1), first subparagraph, first, second and third indent |
|
|
Article 62, first subparagraph, points (a), (b) and (c) |
|
|
|
|
|
Article 9(1), second subparagraph |
|
|
Article 62, second subparagraph |
|
|
|
|
|
Article 9(1), third subparagraph |
|
|
Annex VII, Part 8, point 4 |
|
|
|
|
|
Article 9(2) |
|
|
Article 63(3) |
|
|
|
|
|
Article 9(3) |
|
|
Annex VII, Part 8, point 1 |
|
|
|
|
|
Article 9(4) |
|
|
Annex VII, Part 8, point 2 |
|
|
|
|
|
Article 9(5) |
|
|
Annex VII, Part 8, point 3 |
|
|
|
|
|
Article 10 |
Article 4(9) |
|
Article 8(2) |
|
|
|
|
|
Article 11(1), third to sixth sentences |
|
|
— |
|
|
|
|
|
Article 12(1), second subparagraph |
|
|
Article 65(1), first subparagraph |
|
|
|
|
|
Article 12(1), third subparagraph |
|
|
Article 65(1), second subparagraph |
|
|
|
|
|
Article 12(2) |
|
|
Article 65(2) |
|
|
|
|
|
Article 12(3) |
|
|
Article 65(3) |
|
|
|
|
|
Article 13(2) and (3) |
|
|
— |
|
|
|
|
|
Article 14 |
Article 19 |
Article 16 |
Article 79 |
|
|
|
|
|
Annex I, first and second sentence of introductory wording |
|
|
Article 56 |
|
|
|
|
|
Annex I, third sentence of introductory wording and list of activities |
|
|
Annex VII, Part 1 |
|
|
|
|
|
Annex IIA |
|
|
Annex VII, Parts 2 and 3 |
|
|
|
|
|
Annex IIA, Part II, last sentence of paragraph 6 |
|
|
— |
|
|
|
|
|
Annex IIB, point 1, first and second sentences |
|
|
Article 59(1), first subparagraph, point (b) |
|
|
|
|
|
Annex IIB, point 1, third sentence |
|
|
Article 59(1), second subparagraph |
|
|
|
|
|
Annex IIB, point 2 |
|
|
Annex VII, Part 5 |
|
|
|
|
|
Annex IIB, point 2, second subparagraph (i) and table |
|
|
— |
|
|
|
|
|
Annex III, point 1 |
|
|
— |
|
|
|
|
|
Annex III, point 2 |
|
|
Annex VII, Part 7, point 1 |
|
|
|
|
|
Annex III, point 3 |
|
|
Annex VII, Part 7, point 2 |
|
|
|
|
|
Annex III, point 4 |
|
|
Annex VII, Part 7, point 3 |
|
|
|
|
|
|
Article 1, first paragraph |
|
Article 42 |
|
|
|
|
|
|
Article 1, second paragraph |
|
— |
|
|
|
|
|
|
Article 2(1) |
|
Article 42(1), first subparagraph |
|
— |
— |
— |
— |
— |
— |
— |
Article 42(1), second to fifth subparagraphs |
|
|
|
|
|
|
Article 2(2), introductory wording |
|
Article 42(2), introductory wording |
|
|
|
|
|
|
Article 2(2)(a), introductory wording |
|
Article 42(2)(a), introductory wording |
|
|
|
|
|
|
Article 2(2)(a), points (i) to (v) |
|
Article 42(2)(a), point (i) |
|
|
|
|
|
|
Article 2(2)(a), point (vi) |
|
Article 42(2)(a), point (ii) |
|
|
|
|
|
|
Article 2(2)(a), point (vii) |
|
Article 42(2)(a), point (iii) |
|
|
|
|
|
|
Article 2(2)(a), point (viii) |
|
Article 42(2)(a), point (iv) |
|
|
|
|
|
|
Article 2(2)(b) |
|
Article 42(2)(b) |
|
|
|
|
|
|
Article 3(2), first subparagraph |
|
Article 3(38) |
|
|
|
|
|
|
Article 3(2), second subparagraph |
|
— |
|
|
|
|
|
|
Article 3(3) |
|
Article 3(39) |
|
|
|
|
|
|
Article 3(4), first subparagraph |
|
Article 3(40) |
|
|
|
|
|
|
Article 3(4), second subparagraph |
|
Article 42(1), third subparagraph |
|
— |
— |
— |
— |
— |
— |
— |
Article 42(1), fourth subparagraph |
|
|
|
|
|
|
Article 3(5), first subparagraph |
|
Article 3(41) |
|
|
|
|
|
|
Article 3(5), second subparagraph |
|
Article 42(1), fifth subparagraph |
|
|
|
|
|
|
Article 3(5), third subparagraph |
|
Article 42(1), third subparagraph |
|
|
|
|
|
|
Article 3(6) |
|
Annex VI, Part 1, point (a) |
|
|
|
|
|
|
Article 3(7) |
|
Article 3(42) |
|
— |
— |
— |
— |
— |
— |
— |
Annex VI, Part 1, point (b) |
|
|
|
|
|
|
Article 3(10) |
|
Article 3(43) |
|
|
|
|
|
|
Article 3(13) |
|
Article 43 |
|
|
|
|
|
|
Article 4(2) |
|
Article 44 |
|
|
|
|
|
|
Article 4(4), introductory wording and points (a) and (b) |
|
Article 45(1), introductory wording and points (a) and (b) |
|
|
|
|
|
|
Article 4(4), point (c) |
|
Article 45(1), point (e) |
|
|
|
|
|
|
Article 4(5) |
|
Article 45(2) |
|
|
|
|
|
|
Article 4(6) |
|
Article 45(3) |
|
|
|
|
|
|
Article 4(7) |
|
Article 45(4) |
|
|
|
|
|
|
Article 4(8) |
|
Article 54 |
|
|
|
|
|
|
Article 5 |
|
Article 52 |
|
|
|
|
|
|
Article 6(1), first subparagraph |
|
Article 50(1) |
|
|
|
|
|
|
Article 6(1), second subparagraph and 6(2) |
|
Article 50(2) |
|
|
|
|
|
|
Article 6(1), third subparagraph |
|
Article 50(3), first subparagraph |
|
|
|
|
|
|
Article 6(1), first part of fourth subparagraph |
|
— |
|
|
|
|
|
|
Article 6(1), second part of fourth subparagraph |
|
Article 50(3), second subparagraph |
|
|
|
|
|
|
Article 6(3) |
|
Article 50(4) |
|
|
|
|
|
|
Article 6(4), first and second sentences of first subparagraph and Article 6(4), first and second sentences of second subparagraph |
|
Article 51(1) |
|
|
|
|
|
|
Article 6(4), third sentence of first subparagraph |
|
Article 51(2) |
|
— |
— |
— |
— |
— |
Article 6(4), third sentence of second subparagraph |
— |
Article 51(3), first subparagraph |
|
|
|
|
|
|
Article 6(4), third subparagraph |
|
Article 51(3), second subparagraph |
|
|
|
|
|
|
Article 6(4), fourth subparagraph |
|
Article 51(4) |
|
|
|
|
|
|
Article 6(5), first part of sentence |
|
— |
|
|
|
|
|
|
Article 6(5), second part of the sentence |
|
Article 46(1) |
|
|
|
|
|
|
Article 6(6) |
|
Article 50(5) |
|
|
|
|
|
|
Article 6(7) |
|
Article 50(6) |
|
|
|
|
|
|
Article 6(8) |
|
Article 50(7) |
|
|
|
|
|
|
Article 7(1) and Article 7(2), first subparagraph |
|
Article 46(2), first subparagraph |
|
|
|
|
|
|
Article 7(2), second subparagraph |
|
Article 46(2), second subparagraph |
|
|
|
|
|
|
Article 7(3) and Article 11(8), first subparagraph, introductory wording |
|
Annex VI, Part 6, first part of point 2.7 |
|
|
|
|
|
|
Article 7(4) |
|
Article 46(2), second subparagraph |
|
|
|
|
|
|
Article 7(5) |
|
— |
|
|
|
|
|
|
Article 8(1) |
|
Article 45(1), point (c) |
|
|
|
|
|
|
Article 8(2) |
|
Article 46(3) |
|
|
|
|
|
|
Article 8(3) |
|
— |
|
|
|
|
|
|
Article 8(4), first subparagraph |
|
Article 46(4), first subparagraph |
|
|
|
|
|
|
Article 8(4), second subparagraph |
|
Annex VI, Part 6, point 3.2 |
|
|
|
|
|
|
Article 8(4), third subparagraph |
|
— |
|
|
|
|
|
|
Article 8(4), fourth subparagraph |
|
— |
|
|
|
|
|
|
Article 8(5) |
|
Article 46(4), second and third subparagraph |
|
|
|
|
|
|
Article 8(6) |
|
Article 45(1), points (c) and (d) |
|
|
|
|
|
|
Article 8(7) |
|
Article 46(5) |
|
|
|
|
|
|
Article 8(8) |
|
— |
|
|
|
|
|
|
Article 9, first subparagraph |
|
Article 53(1) |
|
|
|
|
|
|
Article 9, second subparagraph |
|
Article 53(2) |
|
|
|
|
|
|
Article 9, third subparagraph |
|
Article 53(3) |
|
|
|
|
|
|
Article 10(1) and (2) |
|
— |
|
|
|
|
|
|
Article 10(3), first sentence |
|
Article 48(2) |
|
|
|
|
|
|
Article 10(3), second sentence |
|
— |
|
|
|
|
|
|
Article 10(4) |
|
Article 48(3) |
|
|
|
|
|
|
Article 10(5) |
|
Annex VI, Part 6, second part of point 1.3 |
|
|
|
|
|
|
Article 11(1) |
|
Article 48(1) |
|
|
|
|
|
|
Article 11(2) |
|
Annex VI, Part 6, point 2.1 |
|
|
|
|
|
|
Article 11(3) |
|
Annex VI, Part 6, point 2.2 |
|
|
|
|
|
|
Article 11(4) |
|
Annex VI, Part 6, point 2.3 |
|
|
|
|
|
|
Article 11(5) |
|
Annex VI, Part 6, point 2.4 |
|
|
|
|
|
|
Article 11(6) |
|
Annex VI, Part 6, point 2.5, first subparagraph |
|
— |
— |
— |
— |
— |
— |
— |
Annex VI, Part 6, point 2.5, second subparagraph |
|
|
|
|
|
|
Article 11(7), first part of first sentence of first subparagraph |
|
Annex VI, Part 6, point 2.6, introductory wording |
|
|
|
|
|
|
Article 11(7), second part of first sentence of first subparagraph |
|
Annex VI, Part 6, point 2.6(a) |
|
|
|
|
|
|
Article 11(7), second sentence of first subparagraph |
|
— |
|
|
|
|
|
|
Article 11(7), second subparagraph |
|
— |
|
|
|
|
|
|
Article 11(7), point (a) |
|
Annex VI, Part 6, point 2.6(b) |
|
|
|
|
|
|
Article 11(7), points (b) and (c) |
|
— |
|
|
|
|
|
|
Article 11(7), point (d) |
|
Annex VI, Part 6, point 2.6(c) |
|
|
|
|
|
|
Article 11(7), points (e) and (f) |
|
— |
|
|
|
|
|
|
Article 11(8), first subparagraph, points (a) and (b) |
|
Annex VI, Part 3, point 1 |
|
|
|
|
|
|
Article 11(8), first subparagraph, point (c) and second subparagraph |
|
Annex VI, Part 6, second subparagraph of point 2.7 |
|
|
|
|
|
|
Article 11(8), first subparagraph, point (d) |
|
Annex VI, Part 4, point 2.1, second subparagraph |
|
|
|
|
|
|
Article 11(9) |
|
Article 48(4) |
|
|
|
|
|
|
Article 11(10) |
|
Annex VI, Part 8, point 1.1 |
|
|
|
|
|
|
Article 11(11) |
|
Annex VI, Part 8, point 1.2 |
|
|
|
|
|
|
Article 11(12) |
|
Annex VI, Part 8, point 1.3 |
|
|
|
|
|
|
Article 11(13) |
|
Article 48(5) |
|
— |
— |
— |
— |
— |
— |
— |
Article 49 |
|
|
|
|
|
|
Article 11(14) |
|
Annex VI, Part 6, point 3.1 |
|
|
|
|
|
|
Article 11(15) |
|
Article 45(1), point (e) |
|
|
|
|
|
|
Article 11(16) |
|
Annex VI, Part 8, point 2 |
|
|
|
|
|
|
Article 11(17) |
|
Article 8(2), point (a) |
|
|
|
|
|
|
Article 12(1) |
|
Article 55(1) |
|
|
|
|
|
|
Article 12(2), first and second sentence |
|
Article 55(2) |
|
|
|
|
|
|
Article 12(2), third sentence |
|
Article 55(3) |
|
|
|
|
|
|
Article 13(1) |
|
Article 45(1), point (f) |
|
|
|
|
|
|
Article 13(2) |
|
Article 47 |
|
|
|
|
|
|
Article 13(3) |
|
Article 46(6) |
|
|
|
|
|
|
Article 13(4) |
|
Annex VI, Part 3, point 2 |
|
|
|
|
|
|
Article 14 |
|
— |
|
|
|
|
|
|
Article 15 |
|
— |
|
|
|
|
|
|
Article 16 |
|
— |
|
|
|
|
|
|
Article 20 |
|
— |
|
|
|
|
|
|
Annex I |
|
Annex VI, Part 2 |
|
|
|
|
|
|
Annex II, first part (without numbering) |
|
Annex VI, Part 4, point 1 |
|
|
|
|
|
|
Annex II, point 1, introductory wording |
|
Annex VI, Part 4, point 2.1 |
|
|
|
|
|
|
Annex II, points 1.1 and 1.2 |
|
Annex VI, Part 4, points 2.2 and 2.3 |
|
— |
— |
— |
— |
— |
— |
— |
Annex VI, Part 4, point 2.4 |
|
|
|
|
|
|
Annex II, point 1.3 |
|
— |
|
|
|
|
|
|
Annex II, point 2.1 |
|
Annex VI, Part 4, point 3.1 |
|
— |
— |
— |
— |
— |
— |
— |
Annex VI, Part 4, point 3.2 |
|
|
|
|
|
|
Annex II, point 2.2 |
|
Annex VI, Part 4, point 3.3 and 3.4 |
|
|
|
|
|
|
Annex II, point 3 |
|
Annex VI, Part 4, point 4 |
|
|
|
|
|
|
Annex III |
|
Annex VI, Part 6, point 1 |
|
|
|
|
|
|
Annex IV, table |
|
Annex VI, Part 5 |
|
|
|
|
|
|
Annex IV, final sentence |
|
— |
|
|
|
|
|
|
Annex V, point (a), table |
|
Annex VI, Part 3, point 1.1 |
|
|
|
|
|
|
Annex V, point (a), final sentences |
|
— |
|
|
|
|
|
|
Annex V, point (b), table |
|
Annex VI, Part 3, point 1.2 |
|
|
|
|
|
|
Annex V, point (b), final sentence |
|
— |
|
|
|
|
|
|
Annex V, point (c) |
|
Annex VI, Part 3, point 1.3 |
|
|
|
|
|
|
Annex V, point (d) |
|
Annex VI, Part 3, point 1.4 |
|
|
|
|
|
|
Annex V, point (e) |
|
Annex VI, Part 3, point 1.5 |
|
|
|
|
|
|
Annex V, point (f) |
|
Annex VI, Part 3, point 3 |
|
|
|
|
|
|
Annex VI |
|
Annex VI, Part 7 |
|
|
|
|
|
|
|
Article 1 |
Article 28, first subparagraph |
|
|
|
|
|
|
|
Article 2(2) |
Annex V, Part 1, point 1 and Part 2, point 1, first subparagraph |
|
— |
— |
— |
— |
— |
— |
— |
Annex V, Part 1, point 1 and Part 2, point 1, second subparagraph |
|
|
|
|
|
|
|
Article 2(3) second part |
Annex V, Part 1, point 1 and Part 2, point 1, first subparagraph |
|
— |
— |
— |
— |
— |
— |
— |
Annex V, Part 1, point 1 and Part 2, point 1, second subparagraph |
|
|
|
|
|
|
|
Article 2(4) |
— |
|
|
|
|
|
|
|
Article 2(6), first part |
Article 3(24) |
|
|
|
|
|
|
|
Article 2(6), second part |
Article 28, second subparagraph, point (j) |
|
|
|
|
|
|
|
Article 2(7), first subparagraph |
Article 3(25) |
|
|
|
|
|
|
|
Article 2(7), second subparagraph, first sentence |
— |
|
|
|
|
|
|
|
Article 2(7), second subparagraph, second sentence and points (a) to (i) |
Article 28, second subparagraph and points (a) to (i) |
|
|
|
|
|
|
|
Article 2(7), second subparagraph, point (j) |
— |
|
|
|
|
|
|
|
Article 2(7), third subparagraph |
— |
|
— |
— |
— |
— |
— |
— |
— |
Article 29(1) |
|
|
|
|
|
|
|
Article 2(7), fourth subparagraph |
Article 29(2) |
|
— |
— |
— |
— |
— |
— |
— |
Article 29(3) |
|
|
|
|
|
|
|
Article 2(8) |
Article 3(32) |
|
|
|
|
|
|
|
Article 2(9) |
— |
|
|
|
|
|
|
|
Article 2(10) |
— |
|
|
|
|
|
|
|
Article 2(11) |
Article 3(31) |
|
|
|
|
|
|
|
Article 2(12) |
Article 3(33) |
|
|
|
|
|
|
|
Article 2(13) |
— |
|
|
|
|
|
|
|
Article 3 |
— |
|
|
|
|
|
|
|
Article 4(1) |
— |
|
|
|
|
|
|
|
Article 4(2) |
— |
|
|
|
|
|
|
|
Article 4(3)to 4(8) |
|
|
|
|
|
|
|
|
Article 5(1) |
Annex V, Part 1, point 2, second subparagraph |
|
|
|
|
|
|
|
|
Annex V, Part 1, point 2, first, third and fourth subparagraphs |
|
|
|
|
|
|
|
Article 5(2) |
— |
|
|
|
|
|
|
|
Article 6 |
— |
|
|
|
|
|
|
|
Article 7(1) |
Article 37 |
|
|
|
|
|
|
|
Article 7(2) |
Article 30(5) |
|
|
|
|
|
|
|
Article 7(3) |
Article 30(6) |
|
|
|
|
|
|
|
Article 8(1) |
Article 40(1) |
|
|
|
|
|
|
|
Article 8(2), first part of first subparagraph |
Article 40(2), first part of first subparagraph |
|
|
|
|
|
|
|
Article 8(2), second part of first subparagraph |
— |
|
— |
— |
— |
— |
— |
— |
— |
Article 40(2), second part of first subparagraph |
|
— |
— |
— |
— |
— |
— |
— |
Article 40(2), second subparagraph |
|
— |
— |
— |
— |
— |
— |
— |
Article 40(3) |
|
— |
— |
— |
— |
— |
— |
— |
Article 41 |
|
|
|
|
|
|
|
Article 8(2), second subparagraph |
— |
|
|
|
|
|
|
|
Article 8(3) and (4) |
— |
|
|
|
|
|
|
|
Article 9 |
Article 30(1) |
|
— |
— |
— |
— |
— |
— |
— |
Article 30(2), (3) and (4) |
|
|
|
|
|
|
|
Article 9a |
Article 36 |
|
|
|
|
|
|
|
Article 10, first paragraph, first sentence |
Article 30(7), first sentence |
|
— |
— |
— |
— |
— |
— |
— |
Article 30(7), second sentence |
|
— |
— |
— |
— |
— |
— |
— |
Article 30(8) and (9) |
|
— |
— |
— |
— |
— |
— |
— |
Article 31 to 35 |
|
|
|
|
|
|
|
Article 10, first paragraph, second sentence |
— |
|
|
|
|
|
|
|
Article 10, second paragraph |
— |
|
|
|
|
|
|
|
Article 12, first sentence |
Article 38(1) |
|
|
|
|
|
|
|
Article 12, second sentence |
— |
|
— |
— |
— |
— |
— |
— |
— |
Article 38(2), (3) and (4) |
|
— |
— |
— |
— |
— |
— |
— |
Article 39 |
|
|
|
|
|
|
|
Article 13 |
Annex V, Part 3, third part of point 8 |
|
|
|
|
|
|
|
Article 14 |
Annex V, Part 4 |
|
— |
— |
— |
— |
— |
— |
— |
Annex V, Part 5, 6 and 7 |
|
|
|
|
|
|
|
Article 15 |
— |
|
|
|
|
|
|
|
Article 18(2) |
— |
|
|
|
|
|
|
|
Annex I |
— |
|
|
|
|
|
|
|
Annex II |
— |
|
|
|
|
|
|
|
Annex III and IV |
Annex V, point 2 of Part 1 and Part 2 |
|
|
|
|
|
|
|
Annex V A |
Annex V, Part 1, point 3 |
|
|
|
|
|
|
|
Annex V B |
Annex V, Part 2, point 3 |
|
|
|
|
|
|
|
Annex VI A |
Annex V, Part 1, points 4 and 6 |
|
— |
— |
— |
— |
— |
— |
— |
Annex V, Part 1, point 5 |
|
|
|
|
|
|
|
Annex VI B |
Annex V, Part 2, points 4 and 6 |
|
— |
— |
— |
— |
— |
— |
— |
Annex V, Part 2, point 5 |
|
|
|
|
|
|
|
Annex VII A |
Annex V, Part 1, points 7 and 8 |
|
|
|
|
|
|
|
Annex VII B |
Annex V, Part 2, points 7 and 8 |
|
|
|
|
|
|
|
Annex VIII A point 1 |
— |
|
|
|
|
|
|
|
Annex VIII A point 2 |
Annex V, Part 3, first part of point 1 and points 2, 3 and 5 |
|
— |
— |
— |
— |
— |
— |
— |
Annex V, Part 3, second part of point 1 |
|
— |
— |
— |
— |
— |
— |
— |
Annex V, Part 3, point 4 |
|
|
|
|
|
|
|
Annex VIII A point 3 |
— |
|
|
|
|
|
|
|
Annex VIII A point 4 |
Annex V, Part 3, point 6 |
|
|
|
|
|
|
|
Annex VIII A point 5 |
Annex V, Part 3, points 7 and 8 |
|
|
|
|
|
|
|
Annex VIII A point 6 |
Annex V, Part 3, points 9 and 10 |
|
— |
— |
— |
— |
— |
— |
— |
Annex V, Part 3, point 11 |
|
— |
— |
— |
— |
— |
— |
— |
Annex V, Part 4 |
|
|
|
|
|
|
|
Annex VIII B |
— |
|
|
|
|
|
|
|
Annex VIII C |
— |
|
|
|
|
Annex VI |
|
|
Annex IX |
Annex IX |
|
|
|
|
Annex VII |
|
|
Annex X |
Annex X |