EUROPEAN COMMISSION Strasbourg, 5.4.2022 COM(2022) 156 final/3 2022/0104(COD) CORRIGENDUM

This document corrects document COM(2022)156 final/2

Concerns the EN version only

Correction of typos and formatting issues

The text shall read as follows: Proposal for a DIRECTIVE OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL amending

Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial emissions (integrated pollution prevention and control) and Council Directive 1999/31/EC of 26 April 1999 on the landfill of waste



(Text with EEA relevance) {SEC(2022) 169 final} - {SWD(2022) 110 final} - {SWD(2022) 111 final} - {SWD(2022) 112 final}







TABLE OF CONTENTS EXPLANATORY MEMORANDUM 3 1.CONTEXT OF THE PROPOSAL3 2.LEGAL BASIS, SUBSIDIARITY AND PROPORTIONALITY9 3.RESULTS OF EX-POST EVALUATIONS, STAKEHOLDER CONSULTATIONS AND IMPACT ASSESSMENTS10 4.BUDGETARY IMPLICATIONS13 5.OTHER ELEMENTS14 DIRECTIVE OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL amending Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial emissions (integrated pollution prevention and control) and Council Directive 1999/31/EC on the landfill of waste20 LEGISLATIVE FINANCIAL STATEMENT 51 1.FRAMEWORK OF THE PROPOSAL/INITIATIVE51 1.1.Title of the proposal/initiative51 1.2.Policy area(s) concerned51 1.3.The proposal/initiative relates to:51 1.4.Objective(s)51 1.4.1.General objective(s)51 1.4.2.Specific objective(s)51 1.4.3.Expected result(s) and impact52

1.4.4.Indicators of performance52 1.5.Grounds for the proposal/initiative53 1.5.1.Requirement(s) to be met in the short or long term including a detailed timeline for roll-out of the implementation of the initiative53 1.5.2.Added value of Union involvement.54 1.5.3.Lessons learned from similar experiences in the past54 1.5.4.Compatibility with the Multiannual Financial Framework and possible synergies with other appropriate instruments55 1.5.5.Assessment of the different available financing options, including scope for redeployment55 1.6.Duration and financial impact of the proposal/initiative58 1.7.Management mode(s) planned58 2.MANAGEMENT MEASURES58 2.1.Monitoring and reporting rules58 2.2.Management and control system(s)59 2.2.1.Justification of the management mode(s), the funding implementation mechanism(s), the payment modalities and the control strategy proposed59 2.2.2.Information concerning the risks identified and the internal control system(s) set up to mitigate them59 2.2.3.Estimation and justification of the cost-effectiveness of the controls (ratio of "control costs ÷ value of the related funds managed"), and assessment of the expected levels of risk of error (at payment & at closure)59 2.3.Measures to prevent fraud and irregularities59 3.ESTIMATED FINANCIAL IMPACT OF THE PROPOSAL/INITIATIVE59 3.1.Heading(s) of the multiannual financial framework and expenditure budget line(s) affected59 3.2.Estimated financial impact of the proposal on appropriations60 3.2.1.Summary of estimated impact on operational appropriations60

3.2.2.Estimated output funded with operational appropriations -64 3.2.3.Estimated impact on ECHA resources66 3.2.3.1.Estimated requirements of human resources in the Commission67 3.2.4.Compatibility with the current multiannual financial framework67 3.2.5.Third-party contributions68 3.3.Estimated impact on revenue68 EXPLANATORY MEMORANDUM 1.CONTEXT OF THE PROPOSAL • Reasons for and objectives of the proposal Directive 2010/75/EU on industrial emissions (‘the IED’) regulates the environmental impacts of around 52 000 of Europe’s large-scale, high-pollution-risk industrial installations and livestock farms (‘agro-industrial installations’) in an integrated manner, on a sector-by-sector basis. It covers all relevant pollutants potentially emitted by agro-industrial installations that affect human health and the environment. Installations regulated by the IED account for about 20% of the EU’s overall pollutant emissions by mass into the air, around 20% of pollutant emissions into water and approximately 40% of greenhouse gas (GHG) emissions. Activities regulated by the IED include power plants, refineries, waste treatment and incineration, production of metals, cement, glass, chemicals, pulp and paper, food and drink, and the intensive rearing of pigs and poultry. An installation regulated by the IED may carry out several IED activities, e.g. cement production and waste co-incineration. The 2020 evaluation of the IED concluded that it was generally effective in preventing and controlling pollution into air, water and soil from industrial activities, and in promoting the use of best available techniques (BAT). The IED has substantially reduced emissions of pollutants into the air and, to a lesser degree, water emissions. It has also helped reducing emissions into the soil from IED installations. Although its impacts on resource efficiency, the circular economy and innovation are harder to assess, the Directive appears to have made a positive contribution, albeit of limited magnitude. It has also made a limited contribution to decarbonisation, within the constraints currently placed on the IED. Other aspects, such as public access to information and access to justice, have improved compared to the earlier legislation that the IED replaced. However, the evaluation also identified several areas for improvement, in light of new challenges. It showed that, while it provides a sound framework, the Directive is not being implemented consistently across Member States, with different levels of ambition preventing the instrument from fully delivering on its objectives. These challenges undermine the Directive's capacity to reduce the environmental pressures exerted by agro-industrial installations and set a level playing field that provides a high level of protection of human health and the environment. As concluded by the European Court of Auditors, these issues also affect the IED's capacity to implement the ‘polluter pays’ principle in an appropriate manner. To address those challenges and incentivise the deep industrial transformation required between 2025 and 2050, the Commission committed in the European Green Deal (EGD) to revise EU measures to address pollution from large agro-industrial installations. Moreover, the Union is committed to the 2030 Agenda for Sustainable Development and its Sustainable Development Goals. This proposal contributes to several of the SDGs. This initiative's general objective is to help, in the most effective and efficient way, protect ecosystems and human health from the adverse effects of pollution from large agro-industrial installations and improve EU industry’s resilience to the impacts of climate change. The revision of the IED aims to stimulate a deep agro-industrial transformation towards zero pollution through the use of breakthrough technologies, thereby contributing to the EGD's objectives of reaching carbon neutrality, increased energy efficiency, a non-toxic environment and a circular economy. It also aims to continue supporting the creation of a competitive level playing field providing a high level of protection of human health and the environment. In addition, the IED revision will seek to modernise and simplify the current legislation, e.g. through digitalisation and improving knowledge about sources of pollution. The initiative will also aim to improve public participation in decision-making and increase access to information and justice, including to effective redress mechanisms. More specifically, the revision of the Directive will seek to: ‘ i. improve IED effectiveness in preventing or, when impractical, minimising the emission of pollutants by agro-industrial installations at source, as evidenced by continued or accelerated decreasing trends of emission levels, to avoid or reduce adverse impacts on health and the environment, taking into account the state of environment in the area affected by these emissions; ii. ensure access by private individuals and civil society to information, participation in decision-making, and access to justice (including effective redress) in relation to permitting, operation and control of the regulated installations, resulting in increased civil society action; iii. clarify and simplify the legislation and reduce administrative burden while promoting consistency of implementation by the Member States; iv. promote the uptake of innovative technologies and techniques during the ongoing industrial transformation, by revising BAT reference documents (BREFs) without delay, when there is evidence that better performing innovative techniques become available, and ensuring permits support frontrunners; v. support the transition towards the use of safer and less toxic chemicals, improved resource efficiency (energy, water and waste prevention) and greater circularity;

vi. support decarbonisation by fostering synergies in the use of and investments in techniques that prevent or reduce pollution and carbon emissions, as evidenced by a coupling of the trends in emission intensities; vii. address the harmful impacts on health and the environment from agro-industrial activities currently not regulated by the IED, as evidenced by decreasing trends of emission intensity.’ The Council and the European Parliament,, welcomed the revision of the IED and expressed their expectations that this revision should address pollutant emissions into the air from industrial and agricultural activities and contribute to the circular economy, including by promoting water reuse in industry,. The European Citizens Panel on climate change and environment has adopted clear recommendations in this respect in the framework of the Conference on the Future of Europe. In that context, European citizens have expressed manifest support for the EU to tackle the pollution of water, soil and air and to reduce methane emissions, and they emphasize the responsibilities of the polluters. The multi-stakeholder High Level Group on Energy-Intensive Industries, advising the Commission on policies relevant to energy-intensive industries since 2015, developed a masterplan setting out recommendations to build the policy framework needed to manage this transition while keeping industry competitive. It recommended that ‘the Industrial Emissions Directive permitting process should be adapted to support GHG abatement measures in energy-intensive installations throughout the transition.’ • Consistency with existing policy provisions in the policy area The EGD is Europe’s growth strategy to ensure a climate-neutral, clean and circular economy by 2050, optimising resource management and energy efficiency, and minimising pollution, while recognising the need for deeply transformative policies in line with the Energy Efficiency First principle. The EU chemicals strategy for sustainability of October 2020 and the zero pollution action plan adopted in May 2021 specifically address the pollution aspects of the EGD. In parallel, the new industrial strategy for Europe highlights the need for research, innovation and investments for new technologies to strengthen Europe’s industrial competitiveness and facilitate industry’s shift to a truly sustainable, greener, efficient and more digital economy. The updated May 2021 version of this strategy further emphasises the potential role of transformative technologies. Other particularly relevant policies include the ‘fit for 55’ package, the methane strategy and the Glasgow methane pledge, the climate adaptation strategy, the biodiversity strategy, the ‘farm to fork’ strategy, the soil strategy and the sustainable products initiative. In the EGD, the Commission commits to revising EU measures to address pollution from large industrial installations. It does this notably by looking at the scope of the legislation and at how to make EU legislation in this area fully consistent with the zero pollution ambition, and climate, energy and circular economy policies, bearing in mind the benefits for both public health and biodiversity. The IED and Regulation (EC) No 166/2006 on the European Pollutant Release and Transfer Register (‘the E-PRTR Regulation’) are complementary instruments regulating the environmental impact of industry. The IED aims to secure a progressive reduction in pollution from the EU’s largest agro-industrial installations, while preserving a competitive level playing field. The E-PRTR Regulation facilitates the monitoring of pollution-reduction efforts by improving publicly available information on the actual performance of installations. This legislation has links with many other policies since it seeks to address the environmental pressures from agro-industrial installations in a holistic manner. The IED has played an important role in reducing emissions of pollutants from industry, especially to the air, but has made a more limited contribution to the circular economy (resource efficiency) and to reducing emissions of pollutants into water. Water is one of the three main pillars of the ‘zero pollution action plan’, which aims to achieve a toxin-free society by 2050, with pollution reduced to either zero, or levels that are no longer harmful for nature and humans. This implies action not only downstream, such as at the level of wastewater treatment plants, but also upstream, where substances are produced and used. This proposal to revise the IED is consistent with EU water legislation, in particular Directive 2000/60/EC (the Water Framework Directive), and its two related directives, Directive 2006/118/EC (on groundwater) and Directive 2008/105/EC, as amended by Directive 2013/39/EC, on environmental quality standards in the field of water policy. EU water legislation obliges Member States to avoid deterioration in the status of all water bodies and to achieve good status for all water bodies, through a system of integrated water management per river basin. Through six-yearly management cycles, ecological and chemical status (surface waters) and quantitative and chemicals status (groundwater) are assessed and measures are planned to address all pressures on water bodies, including from agriculture, industry, households and other economic activities (including navigation, flood protection and hydropower). In light of the zero pollution action plan, the Commission has announced that it will formulate a proposal in 2022 to further tighten rules on surface and groundwater pollutants, as part of a legislative proposal on ‘integrated water management’. The IED proposal complements these initiatives by, among others, widening the Directive’s scope, encouraging the development of new technologies to reduce emissions, improving resource and energy efficiency, promoting water reuse, ensuring better controlled and more integrated permitting requirements, and introducing a mandatory environmental management system. The proposal will strengthen the integrated approach by clarifying requirements for cooperation between relevant competent authorities. This cooperation includes reviewing and updating permits, depending on the status of the receiving environment, and/or planning measures to comply with environmental quality standards, objectives, plans and programmes under the water legislation. Increased coherence will also be created by clarifying the rules that apply to the indirect release of polluting substances into water through urban wastewater treatment plants. Fostering innovation will help address persistent chemical substances and substances newly identified as being of concern, including per- and polyfluoroalkyl substances (PFAS), microplastics and pharmaceuticals. This is consistent with the chemicals strategy for sustainability, the European Commission’s Communication on a strategic approach to pharmaceuticals in the environment and the Communication on a pharmaceuticals strategy. The ‘exchange of information’ process under the IED to draw up and review Best Available Technique reference documents (BREFs) should take account of the identification of substances of concern under EU water legislation. In particular, these include ‘watch lists’ of substances for groundwater and surface water, and substances identified as possibly posing a significant risk to or via the aquatic environment at EU level. The exchange of information under the IED will also benefit the development of water efficiency measures and consideration of water reuse by agro-industrial installations, in line with the circular economy action plan, which commits to promoting water reuse in industry. Regulation (EU) 2020/741 on minimum requirements for water reuse, adopted in May 2020, applies to water reuse for agricultural irrigation but it also highlights the great potential for the recycling and reuse of treated wastewater for industrial purposes, as part of integrated water management and the circular economy. By regulating certain activities at source, the IED supports Member States in meeting their obligations under other EU legislation that sets environmental quality standards, such as the Ambient Air Quality Directive. It also supports Member States in meeting their objectives under EU legislation that sets national targets, such as the National Emission Reduction Commitments Directive, the Effort Sharing Regulation, and the Energy Efficiency Directive. The IED’s BAT associated emissions levels were utilised to define the ‘do-no-significant-harm’ criteria for the Taxonomy Climate Delegated Act. The proposed IED revision measures will further support the EU Taxonomy on sustainable investments over time by setting additional and updated criteria. These criteria will be determined with a view to making a substantial contribution to preventing and controlling pollution, with the additional objective of helping the Sustainable Finance Platform to define which activities might be termed as sustainable. Finally, the IED helps to improve general environmental performance, contributing to meeting the objectives of other EU sectoral legislation including in relation to REACH, waste, and the protection of nature. • Consistency with other Union policies

The 8th environment action programme focuses on six interlinked priority objectives. Among these are: ·Article 2(d) – pursuing zero pollution, including in relation to harmful chemicals, in order to achieve a toxin-free environment, including air, water and soil. It also aims to reduce light and noise pollution, and protect the health and well-being of people, animals and ecosystems from environment-related risks and negative impacts. ·Article 2(f) – promoting environmental aspects of sustainability and significantly reducing key environmental and climate pressures related to the EU’s production and consumption. This particularly relates to the areas of energy, industry, buildings and infrastructure, mobility, tourism, international trade and the food system. The IED proposal will help meet these objectives. The new geopolitical and energy market reality requires the Union to drastically accelerate the clean energy transition and increase Europe's energy independence from unreliable suppliers and volatile fossil fuels. As part of the EU response to the 2022 Russia-Ukraine war, the REPowerEU initiative aims to increase the resilience of the EU-wide energy system through a diversification of gas supplies and a reduction of the use of fossil fuels by boosting energy efficiency, increasing renewables and electrification, and addressing infrastructure bottlenecks. The revision of the Directive contributes to the resilience of the EU-wide energy system through improving energy efficiency of industrial processes in the Union. This proposed Directive is a pilot, following the Commission's ‘one in one out’ approach to reduce administrative burden. The supporting impact assessment report provides detailed information on the proposal's expected administrative burden. The section of this memorandum on regulatory fitness and simplification outlines measures proposed to limit the proposal's administrative burden. 2.LEGAL BASIS, SUBSIDIARITY AND PROPORTIONALITY • Legal basis The legal basis for this proposal is Article 192 TFEU. In accordance with Article 191 and 192(1) TFEU, the EU is required to contribute to the pursuit of the following objectives: preserving, protecting and improving the quality of the environment; promoting measures at international level to deal with regional or worldwide environmental problems, and combating climate change. • Subsidiarity (for non-exclusive competence) This Directive's objectives of ensuring a high level of environmental protection and improving environmental quality throughout the Union cannot be sufficiently achieved by Member States. Because of the transboundary nature of pollution from industrial activities, these objectives can be better achieved at EU level, justifying the EU's adoption of measures in accordance with the principle of subsidiarity as set out in Article 5 of the Treaty on European Union. Pollution from agro-industrial installations disperses across national borders and pollution control cannot be sufficiently achieved by one Member State alone. In addition, the operation of industrial plants is closely linked to the functioning of the single market. In the absence of an EU-wide approach for setting environmental performance standards, the same industries would face different pollution control regulations in each Member State, with the risk of creating an uneven playing field, fragmenting the single market and impeding the EU's efforts to pursue the Treaty objective of achieving a high level of environmental and human health protection. • Proportionality The design of the IED ensures proportionality of outcomes by (i) defining BAT as the most environmentally effective and economically viable range of proven techniques used in a sector, and (ii) allowing derogations in individual cases if applying the EU-wide BAT requirements would lead to costs disproportionately higher than the expected environmental/health benefits. The supporting impact assessment assesses the impacts of all proposed revisions of the IED. Both qualitative and quantitative assessment has been undertaken that shows that the proposals are proportionate, i.e. that societal benefits are significantly higher than the costs incurred. The measures with the largest impact were identified as extending the scope to cover cattle farms and a larger number of pig and poultry farms. The monetised health and environmental benefits from reduced methane and ammonia emissions are valued at over EUR 5.5 billion per/year, while the compliance costs are EUR 265 million and administrative costs (administrations and operators) are EUR 223 million, resulting in a very beneficial cost-benefit factor of 11. • Choice of the instrument The proposal's objectives can be best pursued through a Directive. This is the most appropriate legal instrument to make amendments to the existing Directive on Industrial Emissions (Directive 2010/75/EU). A Directive requires Member States to achieve its objectives and implement the measures into their national substantive and procedural law systems. This approach gives Member States more freedom when implementing an EU measure than a Regulation, in that Member States are able to choose the most appropriate means of implementing the measures in the Directive. This allows Member States to ensure that the amended rules are embedded in their substantive and procedural legal framework for implementing the EU IED, in particular regulating permits for installations and enforcement measures and penalties. 3.RESULTS OF EX-POST EVALUATIONS, STAKEHOLDER CONSULTATIONS AND IMPACT ASSESSMENTS

• Ex-post evaluations/fitness checks of existing legislation The evaluation of the IED carried out in 2020 found that it had been effective in reducing environmental impacts and competitive distortions in the EU. The collaborative process for producing BREFs and identifying BAT, also known as the ‘Sevilla Process’, has worked well and is recognised as a model of collaborative governance. The IED has led to substantially reduced pollutant emissions into the air and, to a lesser degree, into water. It reduced emissions into soil from IED installations. Its impacts on resource efficiency, the circular economy and innovation are harder to assess; it appears to have made a positive contribution of limited magnitude. Other aspects, such as public access to information and access to justice, have somewhat improved. The IED was evaluated as largely efficient. The benefits of BAT conclusions substantially outweigh costs. No disproportionate or unnecessary administrative costs have been identified. There are mixed impacts on EU competitiveness; no evidence shows these to be significant. All stakeholder groups considered the IED relevant. It can respond to emerging environmental issues, despite the length of the BREF process. While the IED has not contributed greatly to decarbonisation, views diverge about whether it is relevant to this. The IED was evaluated as being coherent internally and with other EU policies, however there is scope for greater contribution to these. Some interpretation challenges require clarification. The IED was deemed to provide significant EU added value. It ensures more consistent requirements to reduce industrial pollution, including through monitoring and enforcement, reducing single market distortions. Absence of EU action would have led to less demanding standards and fewer health and environment benefits. The BREF process is not replicable by individual Member States, and is increasingly used by non-EU countries. The IED’s decentralised approach is consistent with the subsidiarity and proportionality principles. The evaluation has identified a number of areas where the IED’s performance does not appear to be as satisfactory as desired with regard to reducing pollutant emissions, especially into water, contributing to GHG emission reduction, promoting non-toxic production, and improving resource efficiency and reuse. These areas are central to the revision of the IED announced in the EGD Communication. • Stakeholder consultations The impact assessment accompanying the combined revision of the Industrial Emissions Directive (IED) and E-PRTR Regulation was subject to a thorough consultation process. This included a variety of different consultation activities aimed at gathering the views of all relevant stakeholders and ensuring that the views of different organisations and stakeholder types were considered. Firstly, initial feedback was provided on the published inception impact assessment via the Commission’s ‘Have Your Say’ interactive portal (154 responses; consultation period 24 March 2020 to 21 April 2020). This was followed by a joint IED and E-PRTR public consultation (online survey via the Commission’s ‘Have Your Say’ interactive portal; 336 responses; from 20 December 2020 to 23 March 2021). The survey contained 24 questions, four of which related specifically to the E-PRTR. Then, a targeted stakeholder survey took place from 8 February to 9 April 2021. This consisted of an online survey of a more detailed nature (235 responses), to further improve the evidence base by collecting more specialised feedback from specific stakeholder groups on six problem areas, grouped by the options being considered in the impact assessment study. These problem areas were as follows: i) the environment is polluted; ii) a climate crisis is happening; iii) natural resources are being depleted; iv) state of the art techniques cannot respond satisfactorily to problem areas i) to iii); v) private individuals have limited opportunities to become informed about, and take action regarding impacts caused by agro-industrial plants; and vi) excessive burdens may affect the efficiency of the policy instrument. Feedback received through those surveys was also complemented by consulting focus groups, in June-August 2021, to engage stakeholders in deeper discussions on key themes. Stakeholders were selected based on their sectoral representation and to ensure a good geographical and stakeholder-type distribution between environmental NGOs, industry representatives and Member States’ ministries and competent authorities, to enable balanced discussions. Finally, two stakeholder workshops were held remotely, on 15 December 2020 and 7-8 July 2021. Civil society and environmental NGOs considered all the above problem areas to be of high relevance, in particular in relation to: - the environmental impacts and decarbonisation being insufficiently addressed by the IED; - the need to have the E-PRTR pollutant list updated more quickly to take account of new threats; and - limited access to information on installations’ performance levels. This limited access to information was perceived by all stakeholder groups as an important issue that needs to be addressed.

However, there were differences in the feedback from industry and business associations, who were more neutral (but not negative) in acknowledging issues regarding resource efficiency and less toxic production. Industry and business associations were also more neutral in acknowledging the need to support decarbonisation, highlighting the potential additional reporting costs and risks of overlaps with the Emissions Trading System (ETS). Regarding the Directive's limited scope, industry and business associations noted cost issues, and argued that existing national regimes and EU legislation are sufficient to tackle most of the difficulties encountered. All stakeholders agreed that the IED's contribution to facilitating, harnessing and promoting innovation was too limited. • Impact assessment An impact assessment was carried out, which resulted in a positive opinion from the Regulatory Scrutiny Board dated of 10 December 2021. Five partly interlinked but independent policy options were proposed and assessed; the selected sub-options for each problem area were brought together to form the following preferred policy package: - Effectiveness: full implementation of 24 optimisation and updating measures. - Innovation: frontrunners have freedom to test novel techniques, combined with setting up an innovation centre for industrial transformation and emissions (INCITE) and 2030 operators’ transformation plans. - Resource use and chemicals: improved environmental management system. - Decarbonisation: energy efficiency minimum levels will be introduced, to maximise energy efficiency and minimise energy consumption. A review of the synergies between the IED and the ETS will take place in 2028, allowing optimal synergies from 2030 onwards. - Sectoral scope: additional activities will come into the scope of the IED, principally intensive cattle rearing, and certain extractive activities. The impacts of the preferred package are expected to be as follows. Overall, benefits are expected to considerably outweigh costs. While it has not been possible to quantify and monetise all impacts, is estimated that the set of measures enhancing the effectivenes of the Directive have health benefits between EUR 860 million and EUR 2.8 billion per year with annual business CAPEX/OPEX costs of about EUR 210 million. The overall administrative burden of the whole proposal is estimated at EUR 250 million per year for industrial operators and EUR 196 million per year for public authorities. Extending livestock farms coverage would result in methane and ammonia emission reductions, with related health benefits of over EUR 5.5 billion per year. An extended coverage of the 10% largest cattle farms, representing 41% of emissions of the sector, will lead to a yearly reduction of at least 184 kt of methane and 59 kt of ammonia. Extending the coverage of pig and poultry farms to the largest 18% of pig farms and 15% of poultry farms, representing respectively 85% and 91% of the emissions of the sectors, will reduce yearly emissions at least by 135 kt methane and 33 kt ammonia from pig farms, and 62 kt ammonia from poultry farms. Such increased scope will enhance the IED coverage from 18 to 60% of emissions of ammonia by rearing of cattle, pigs and poultry; and from 3% to 43% of methane emissions. Related compliance costs are estimated to be around EUR 265 million per year. • Regulatory fitness and simplification In line with the Commission’s commitment to better regulation, this proposal has been prepared inclusively, based on full transparency and continuous engagement with stakeholders, listening to external feedback and taking account of external scrutiny to ensure the proposal strikes the right balance. The IED is the result of a better regulation initiative that successfully merged and simplified seven Directives and streamlined administrative aspects, including cutting reporting requirements by around half. Whilst this limits the potential for further streamlining, stakeholder consultations have allowed the Commission to identify a number of potential further clarifications and simplifications to the Directive. Those attracting positive interest from stakeholders will solve uncertainties related to the permitting process. This concerns, in particular, clarifying certain provisions on gasification, liquefaction and pyrolysis that are important activities for achieving a circular low carbon economy. Other aspects involve replacing the indicative list of pollutants in Annex II with references to other EU legislation that sets out lists of relevant pollutants, and establishing harmonised criteria for assessing compliance across the EU. Both measures will enhance legal certainty on the applicable rules for all IED operators. Furthermore, solving discrepancies in compliance assessment approaches used under Chapters II, III and IV of the IED will benefit some 4 000 operators of large combustion plants and waste incinerators. In addition, a separate and lighter permitting regime will be introduced for 20 000 livestock farms currently regulated by the IED as well for those that will be newly brought within its scope, the smallest businesses regulated by the IED; reducing the administrative burden by EUR 113 Million per year. A codification of the legislation after the revised act has been adopted will allow provisions that have become obsolete to be eliminated.

• Fundamental rights The proposal respects the fundamental rights and observes the principles recognised in particular by the Charter of Fundamental Rights of the European Union. Pursuant to Article 52(1) of the Charter, any limitation on the exercise of the rights and freedoms recognised by this Charter must be provided for by law and respect the essence of those rights and freedoms. Subject to the principle of proportionality, limitations may be made only if they are necessary and if they genuinely meet objectives of general interest recognised by the Union or the need to protect the rights and freedoms of others. This proposal strikes the right balance between the fundamental right of freedom to conduct a business and the fundamental right of property and other fundamental rights (environment, health, remedy). The limitation to the right of freedom to conduct a business and the right of property are limited to what is necessary to preserve the other above-mentioned fundamental rights and objectives of general interest in accordance with Article 52(1) of the Charter. The proposal contributes to the objective of a high level of environmental protection in accordance with the principle of sustainable development as laid down in Article 37 of the Charter; to the right to right to life and the integrity of the person and its health as laid down in Articles 2, 3 and 35 of the Charter; and to the right to consumer protection as laid down in Article 38. It also contributes to the right to an effective remedy as laid down in Article 47 of the Charter, in relation to the protection of human health. 4.BUDGETARY IMPLICATIONS The annexed financial statement shows the budgetary implications and the human and administrative resources required. The proposal will have budgetary implications for the Commission and the European Chemicals Agency (ECHA) in terms of human and administrative resources required. The Commission will have an increased number of implementation and enforcement tasks resulting from the increased scope of the economic activities and environmental aspects covered by the IED. The Commission will also have an increased role in managing the innovation centre and wider work to draft BREFs and BAT conclusions, requiring in total 4 additional full-time-equivalent staff. The ECHA will support the Commission by: (1) providing input to the information exchange on BAT and emerging techniques including identifying and selecting relevant substances for each sector, developing sector-specific good practice for the use of the safest substances on the market, and (2) providing tools and guidance for use by IED operators in preparing the chemicals chapter of their environmental management system. This requires a total of 3 additional full-time-equivalent staff. Around EUR 8 200 000 per year is required to finance the necessary expertise to support the Commission in a number of work streams related to INCITE and the drafting of BREFs and BAT conclusions. 5.OTHER ELEMENTS • Implementation plans and monitoring, evaluation and reporting arrangements The overall emissions of pollutants per sector, based on data reported by operators to the E-PRTR, will remain key indicators for tracking progress against this initiative's objectives. The E-PRTR Regulation is being revised in parallel to the revision of this Directive and will allow better future monitoring of the IED’s impact on industry’s environmental performance at sector level. - The increased granularity of reporting of pollutant emission at installation level will allow for analysis of the main processes within sectors whose environmental performance is improving or is lagging behind. - The inclusion of reporting of resource use will allow new indicators to be identified, on use of materials, water and energy, that will enable resource efficiency improvements to be tracked. - More dynamic updating of the list of substances covered by the E-PRTR Regulation will allow emission indicators to be identified for substances of emerging and current concern. This will enable improvements in the use and management of such substances to be tracked. These improvements will also help ensure that this monitoring can be used effectively in the wider zero pollution monitoring and outlook framework, which will be published every 2 years from 2022 onwards. Data on air, water and soil pollution available through zero pollution monitoring will help evaluate the impacts of emission reductions from the installations that fall within scope of the IED and E-PRTR Regulation. A central concern in revising the IED is to ensure that the whole range of BAT-associated emissions levels (AELs) is used. The future standardised permit summary will make it significantly easier to collect the emission limit values (ELVs) set in permits, through automated IT tools. This will allow sector-by-sector analysis of the distribution of ELVs within the BAT-AEL ranges, at the end of the permit revision cycles triggered by the adoption of BAT conclusions and will make the information contained in the permits clearer to the public. The scale of progress in emissions reduction will depend on: technological progress; the outcomes of the innovation centre; any more frequent BREF reviews; and any actions that may be taken as a result. It will also be important to monitor the pace of development and uptake of innovations and the resulting transformation of IED sectors needed to meet the EU’s 2030 and 2050 environmental and climate objectives. The standardised permit summary will allow the number of cases to be quantified where new flexibilities supporting frontrunners in testing and deploying emerging techniques have been used. Wider impacts on innovation dynamics will be more complex to monitor. New indicators will be set out in an industrial transformation scoreboard published by the innovation centre. The centre may develop indicators such as:

- technology readiness level of transformative technologies per sector; - emissions performance of transformative technologies; - the anticipated uptake timeline of such technologies; - distance to target indicators, for each IED sector. Periodic publication of implementation information by Member States will complement these indicators, by providing readily accessible, machine-readable, common-format information on key provisions via dynamic IT means. This will include information on: - the granting of flexibilities to support transformative techniques; - the setting of stricter permit conditions in permits, where required to meet environmental quality standards; - the granting of derogations allowing pollutant emissions higher than the BAT-AEL range; - enforcement action taken. Perceptions on improvements to legal clarity will be monitored via the BREF process, through e-surveys sent to the IED stakeholder community. The review of the interaction between the IED and the ETS and decarbonisation developments, expected to take place before 2030, will be a key milestone in monitoring and evaluating this revamped and more holistic policy approach. • Detailed explanation of the specific provisions of the proposal (a)Amendments to Directive 2010/75/EU The amendment to Article 1 aims at explicitly clarifying that this Directive lays down rules designed to prevent or, where that is not practicable, to reduce emissions into air, water and land and to prevent the generation of waste, in order to achieve a high level of protection of human health and the environment taken as a whole; consistent with Article 191 of the Treaty on the Functioning of the European Union (TFEU). Such explicit clarification is also added in other Articles where necessary. Amendments to Article 3 aim at providing relevant definitions of new concepts or elements which are being added to the Directive by virtue of extension of its scope or strengthening of its provisions. Amendments to Article 5 aim at further specifying transparency requirements attached to permits granted under this Directive, against the background of uneven practice among Member States. Such permits shall be made available to the public on the internet, free of charge and without restricting access to registered users, and a uniform summary of permits shall be made available to the public. Incidents or accidents may affect significantly the environment or human health beyond borders of the national territory of the Member State in which they occur. In such cases, pursuant to amendments to Article 7, immediate transboundary information, as well as multidisciplinary cooperation, must take place. Amendments to Article 8 aim at tightening the rules applying in case of breach of permit conditions and broadening the powers of the competent authority to suspend an installation’s operations until compliance is restored. In respect of combustion units or other units emitting carbon dioxide which are also in the scope of Directive 2003/87/EC establishing a scheme for greenhouse gas emission allowance trading within the Community, the amendment to Article 9 aims at making any requirements relating to energy efficiency mandatory.

Amendments to Article 11 aim at introducing, as part of the basic obligations of the operator, requirements on resource efficiency, on the taking into account of the overall life-cycle environmental performance of the supply chain and on an environmental management system. In the context of the exchange of information leading up to the drawing up and review of BAT reference documents (BREFs), amendments to Article 13 are twofold. First, with a view to developing synergies between the work carried out by the European Chemicals Agency (ECHA) on chemicals and the elaboration of BREFs, it is appropriate to give a formal role to ECHA. Second, the handling of confidential business information (CBI) collected from industry should be specified so as to facilitate the exchange of information supporting the determination of emission levels and environmental performance levels associated with BAT and emerging techniques while preserving the confidentiality of relevant business information. Several amendments are made to Article 14 on permit conditions, with a view to strengthening the requirements attached to permits granted under this Directive; among which a duty for Member States to ensure that all authorities who ensure compliance with EU environmental legislation, including where applicable with environmental quality standards, are duly consulted, before the granting of a permit. Moreover, it is appropriate to refer to Annex II on pollutants of Regulation (EC) No 166/2006 establishing a European Pollutant Release and Transfer Register as being amended. Indeed, by listing individual substances in a non-exhaustive way, Annex II of this Directive on the list of polluting substances is not compatible with the holistic approach sought and the need for competent authorities to take into account all relevant polluting substances, including those of emerging concern. This non-exhaustive list of polluting substances should therefore be deleted. Besides, it is also necessary to clarify the relationship between this Directive and Directive 2006/21/EC of the European Parliament and of the Council of 15 March 2006 on the management of waste from extractive industries. Where the activity referred to in point 3.6 of Annex I to this Directive falls also under the scope of Directive 2006/21/EC, the BAT conclusions established pursuant to Article 13(5) IED will prevail for the purpose of permitting under Directive 2010/75, over BAT as referred to in Article 21(3) of Directive 2006/21/EC. A new Article 14a is inserted in the Directive, requiring the operator to establish and implement an environmental management system (EMS) in accordance with relevant BAT conclusions, with a view to the continuous improvement of the environmental and energy efficient performance and safety of the installation. Article 14a bis also interlinks with the audit obligation under the Energy Efficiency Directive, thus strengthening both proposals. Several improvements are proposed to tighten rules under Article 15. Firstly, the conditions under which the competent authority, when setting emission limit values applicable to pollutant releases to water in an IED permit, may take account of the downstream treatment processes in a waste water treatment plant, are clarified in order to ensure that such releases do not lead to an increased load of pollutants in receiving waters when compared to a situation where the IED installation applies BAT and meets BAT-AELs for direct releases. Secondly, BAT is applied heterogeneously across Member States, industry sectors and even between individual industrial installations; between 75% and 85% of all emission limit values in permits are set at the least demanding end of the BAT-AEL ranges, resulting in under-delivery of emissions reductions. Therefore, competent authorities should set the emission limit values (ELVs) at the lowest end of the relevant BAT-AEL range, unless the operator demonstrates that applying BAT as described in BAT conclusions only allows meeting less strict ELVs. Thirdly, in order to prevent or minimise the emission of pollutants by IED installations and level the playing field across the EU, it is necessary to better frame the conditions under which derogations to emissions limit values can be granted, consistent with principles to be set in an annex to this Directive, and with a standardised methodology for assessing the disproportionality between costs of implementation of BAT conclusions and the potential environmental benefits, to be adopted in an implementing act. Such derogations should not be granted where they may put at risk compliance with environmental quality standards. A new Article 15a is introduced, which empowers the Commission to set common rules for assessing compliance with emission limit values and validation of measured levels for both air and water emissions based on BAT, for installations covered by Chapter II. These compliance assessment rules will take precedent over rules set in Chapters III and IV on assessment of compliance with emission limit values contained in Annexes V and VI. The amendment to Article 16 aims at complementing monitoring requirements in respect of derogations granted under Article 15(4), as regards the concentration of the pollutants concerned by the derogation which are present in the receiving environment. The amendment to Article 18 aims at clarifying that environmental quality standards refer to the requirements set out in Union law, such as EU legislation on air or water; which must be fulfilled at a given time by a given environment or particular part thereof, and that where stricter conditions than those achievable by the use of the BAT by an IED installation are necessary to ensure compliance with such environmental quality standards, specific additional measures must be included in the permit as set out in this article. The amendment to Article 21 aims at clarifying that permit conditions should be reviewed and, where necessary, updated by the competent authority where it is necessary for the installation to comply with an environmental quality standard. Amendments to Article 24 include broadening the cases where the public concerned are given early and effective opportunities to participate in the granting or updating of permit conditions by the competent authority, consistent with the Aarhus Convention. The amendment to Article 25 aims at clarifying that Member States may not restrict legal standing to challenge a decision of a public authority to those members of the public concerned who participated in the preceding administrative procedure to adopt that decision. Amendments to Article 26 seek to strengthen transboundary cooperation, information exchange and public participation in permitting processes. After Article 26, a new Chapter IIa on ‘promoting innovation’ is inserted, comprising Articles 27 to 27d, so as to foster innovation, facilitate the testing and deployment of emerging techniques with improved environmental performance, as well as to set up a dedicated centre to support innovation by collecting and analysing information on innovative techniques and characterise their state of development from research to deployment. The centre will allow BAT to develop a forward looking approach and help industries identifying solutions to decarbonise and reduce pollution. It will over time become a hub to foster innovation dynamics for the industrial transition on all European Green Deal policies. Operators will be required to produce transformation plans by 30 June 2030 as part of their environmental management systems, or later, depending on the activites of Annex I at stake, as a contribution towards achieving EU objectives on a clean, circular and climate neutral economy. Amendments to Article 42 further clarify how to assess whether the cleaned gases or liquids resulting from gasification and pyrolysis of waste are sufficiently purified to be combusted without stricter controls than those applying to clean commercial fuels. A new Chapter VIa on ‘special provisions for rearing of poultry, pigs and cattle’ is inserted after Chapter VI and before Chapter VII, and comprising Articles 70a to 70i. In order to reduce the significant pollutant emissions to air and water caused by such rearing, this Chapter includes lowering the threshold above which pigs and poultry installations are included within the scope of Directive 2010/75/EU; and add cattle farming in this scope, alongside pigs and poultry installations. It also sets specific permitting procedures suited to the sector, mindful of the need to balance the administrative permitting procedures with public information and participation and compliance requirements. Operating Rules for livestock farms will take into consideration not only the nature, type, size and density but also the complexity of these installations and the range of environmental impacts they may have, together with economical aspects. This will allow establishing proportionate requirements for different farming practices (intensive, extensive, organic), including by taking into account the specificities of pasture based cattle rearing systems, where animals are only seasonally reared in indoor installations, while minimising burdens for the sector and the competent authorities. Amendments to Article 73 include setting a five-year frequency according to which the Commission shall submit to the European Parliament and to the Council a report reviewing the implementation of this Directive, the first of which will be due by June 2028. This report will take into account the dynamics of innovation and the review referred to in Article 8 of Directive 2003/87/EC. The amendment to Article 74 empowers the Commission to adopt a delegated act in accordance with Article 290 TFEU in respect of adding an agro-industrial activity to Annex I or Annex I a of this Directive, with a view to ensuring that it meets its objectives to prevent or reduce pollutants emissions and achieve a high level of protection of human health and the environment. The amendments to Article 79 aim at specifying the minimum content of penalties, so that they are effective, proportionate and dissuasive, without prejudice to Directive 2008/99/EC on the protection of the environment through criminal law. A new Article 79a on compensation is introduced, which aims at securing that, where damage to health has occurred, fully or partially as a result of a breach of national measures adopted pursuant to this Directive, the public concerned is able to claim and obtain compensation for that damage from the relevant competent authorities and, where identified, the natural or legal persons responsible for the violation. Amendments to Annex I include bringing within the scope of this Directive the extraction of industrial and metallic minerals, activity which has a significant impact on the environment. Similarly, whilst several of the activities of the batteries value chain are already regulated by this Directive, adding as well in the scope of this instrument large installations undertaking the manufacturing of batteries ensures that all stages of the life-cycle of batteries are covered by the Directive’s requirements, aiming at a more sustainable growth of this industrial sector.

(b)Amendment to Council Directive 1999/31/EC The amendment to Article 1 of Council Directive 1999/31/EC on the landfill of waste aims at allowing the adoption of BAT conclusions on landfills under this Directive. Although landfills are included within the scope of the IED, no BAT conclusions exist for landfills owing to the coverage of this activity under Council Directive 1999/31/EC, pursuant to which its requirements are deemed to constitute BAT. Given technical development and innovation that has taken place since the adoption of Council Directive 1999/31/EC, more effective techniques for protecting human health and the environment are now available. The adoption of BAT conclusions would enable addressing the key environmental issues related to the operation of waste landfills, including significant emissions of methane.



2022/0104 (COD) Proposal for a DIRECTIVE OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL amending

Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial emissions (integrated pollution prevention and control) and Council Directive 1999/31/EC of 26 April 1999 on the landfill of waste



(Text with EEA relevance) THE EUROPEAN PARLIAMENT AND THE COUNCIL OF THE EUROPEAN UNION, Having regard to the Treaty on the Functioning of the European Union, and in particular Article 192(1) thereof, Having regard to the proposal from the European Commission, After transmission of the draft legislative act to the national parliaments, Having regard to the opinion of the European Economic and Social Committee, Having regard to the opinion of the Committee of the Regions, Acting in accordance with the ordinary legislative procedure, Whereas: (1)The European Green Deal is Europe’s strategy to ensure, by 2050, a climate-neutral, clean and circular economy, optimising resource management, minimising pollution while recognising the need for deeply transformative policies. The Union is also committed to the 2030 Agenda for Sustainable Development and its Sustainable Development Goals. The EU Chemicals Strategy for Sustainability of October 2020 and the Zero Pollution Action Plan adopted in May 2021 specifically address pollution aspects of the European Green Deal. In parallel, the New Industrial Strategy for Europe further emphasises the potential role of transformative technologies. Other particularly relevant policies for this initiative include the ‘Fit for 55’ package, the Methane Strategy and the Glasgow methane pledge, the Climate Adaptation Strategy, the Biodiversity Strategy, the Farm to Fork strategy and the Sustainable Products Initiative. Besides, as part of the EU response to the 2022 Russia-Ukraine war, REPowerEU proposes a Joint European Action to support the diversification of energy supplies, accelerate the transition to renewable energy and improve energy efficiency. (2)The European Green Deal announced a revision of Union measures to address pollution from large industrial installations, including reviewing the sectoral scope of the legislation and how to make it fully consistent with climate, energy and circular economy policies. In addition, the Zero Pollution Action Plan, the Circular Economy Action Plan and the Farm to Fork Strategy also call for reducing pollutant emissions at source, including sources not currently within the scope of Directive 2010/75/EU of the European Parliament and of the Council. Addressing pollution from certain agro-industrial activities thus requires their inclusion within the scope of that Directive. (3)The Union’s extractive industry is key to achieving the aims of the European Green Deal and the EU industrial strategy, including its update. Raw materials are of strategic importance for the digital and green transition, the energy, materials and circular economy transformation and to strengthen EU economic resilience. In order to achieve these objectives, sustainable domestic capacities need to be further developed. This requires effective, tailored and harmonised measures to ensure that the best available techniques are established and employed, thus applying processes that are both the most efficient and have the lowest possible impacts on human health and the environment . The governance mechanisms of Directive 2010/75/EU that closely associate industry experts to the development of consensual and tailored environmental requirements will support the sustainable growth of those activities in the Union. The development and availability of commonly agreed standards will level the Union’s playing field while ensuring a high level of protection of human health and the environment. It is therefore appropriate to include those activities within the scope of Directive 2010/75/EU. (4)Rearing of pigs, poultry and cattle cause significant pollutant emissions into the air and water. In order to reduce such pollutant emissions, including ammonia, methane, nitrates and greenhouse gas emissions and thereby improve air, water and soil quality, it is necessary to lower the threshold above which pigs and poultry installations are included within the scope of Directive 2010/75/EU and to include also cattle farming within that scope. Relevant BAT requirements take into consideration the nature, size, density and complexity of these installations, including the specificities of pasture based cattle rearing systems, where animals are only seasonally reared in indoor installations, and the range of environmental impacts they may have. The proportionality requirements in BATs aim to incentivise farmers to implement the necessary transition towards increasingly environmentally friendly agricultural practices.

(5)A significant increase in the number of large-scale installations for the production of batteries for electric vehicles will likely take place within the Union up to 2040, increasing the Union’s share of the global battery production. Whilst several of the activities of the batteries value chain are already regulated by Directive 2010/75/EU and batteries are regulated as products by Regulation (EU) .../... of the European Parliament and of the Council* +., it is still necessary to include in the scope of the Directive large installations manufacturing batteries, ensure that they are also covered by the requirements set out in Directive 2010/75/EU and therefore contribute to a more sustainable growth of batteries manufacturing. Including large installations manufacturing batteries in the scope of Directive 2010/75/EU will improve in a holistic way the sustainability of batteries and minimise their impact on the environment throughout their life cycle. (6)With a view to further strengthening public access to environmental information, it is necessary to clarify that permits for installations granted pursuant to Directive 2010/75/EU are to be made available to the public on the Internet, free of charge and without restricting access to registered users. A uniform summary of permits should also be made available to the public under the same conditions. (7)The impact of pollution, including when caused by incidents or accidents, may extend beyond the territory of a Member State. In such cases, without prejudice to Directive 2012/18/EU of the European Parliament and of the Council, limiting the consequences for human health and the environment of incidents or accidents and preventing further possible incidents or accidents requires prompt information and close coordination between the competent authorities of the Members States which are or may be affected by such events. Therefore, in the event of any incident or accident significantly affecting the environment or human health in another Member State, information and transboundary and multidisciplinary cooperation between the affected Member States should be fostered to limit the consequences for the environment and human health and to prevent further possible incidents or accidents. (8)Member States should also adopt compliance assurance measures to promote, monitor and enforce compliance with obligations placed on natural or legal persons under Directive 2010/75/EU. As part of compliance assurance measures, competent authorities should be able to suspend the operation of an installation where a continued breach of the permit conditions and the non-implementation of the findings of the inspection report pose or risk causing a danger to human health or a significant adverse effect upon the environment, in order to stop that danger. (9)In order to foster energy efficiency of installations within the scope of Directive 2010/75/EU which are carrying out activities listed in Annex I to Directive 2003/87/EC, it is appropriate to submit those installations to energy efficiency requirements in respect of combustion units or other units emitting carbon dioxide on the site. (10)The evaluation of Directive 2010/75/EU concluded that there is a need to strengthen the links between that Directive and Regulation (EC) No 1907/2006, to better address the risks of the use of chemicals in installations whithin the scope of Directive 2010/75/EU. In order to develop synergies between the work carried out by the European Chemicals Agency (ECHA) on chemicals and the preparation of BAT reference documents under Directive 2010/75/EU, ECHA should be given a formal role in such preparation of BAT reference documents. (11)In order to facilitate the exchange of information supporting the determination of emission levels and environmental performance levels associated with best available techniques (BAT), while maintaining the integrity of confidential business information, the procedures for the handling of information qualifying as confidential business information or sensitive commercial information, and as collected from the industry in the context of the exchange of information organised by the Commission for the purpose of drafting, reviewing or updating BAT reference documents should be specified. It should be ensured that individuals participating in the exchange of information do not share information qualifying as confidential business information or sensitive commercial information with any representative of undertakings or trade associations having an economic interest in the concerned industrial activities and related markets. Such exchange of information is without prejudice to Union competition law, in particular Article 101 of the Treaty on the Functioning of the European Union (TFEU). (12)To ensure the protection of human health and the environment as a whole, synergies and coordination with other relevant Union environmental legislation are necessary, at all stages of its implementation.Therefore, all relevant competent authorities that ensure compliance with relevant Union environmental legislation should be duly consulted before the granting of a permit under Directive 2010/75/EU. (13)With a view to continuously improving the environmental performance and safety of the installation, including by preventing waste generation, optimising resource use and water reuse, and preventing or reducing risks associated with the use of hazardous substances, the operator should establish and implement an environmental management system (EMS) in accordance with relevant BAT conclusions, and should make it available to the public. The EMS should also cover the management of risks related to the use of the hazardous substances and an analysis of the possible substitution of hazardous substances by safer alternatives. (14)It is necessary to specify further the conditions under which the competent authority, when setting emission limit values applicable to pollutant releases to water in a permit granted under Directive 2010/75/EU, may take account of the downstream treatment processes in a waste water treatment plant, in order to ensure that such releases do not lead to an increased load of pollutants in receiving waters when compared to a situation where the installation applies BAT and meets emission levels associated with the best available techniques for direct releases. (15)Providing a high level of protection of human health and the environment as a whole requires inter alia the establishment in permits of emission limit values at a level that ensures compliance with the applicable emission levels associated with the best available techniques set out in the BAT conclusions. Emission levels associated with the best available techniques (BAT-AELs) are usually expressed as ranges, rather than as single values, to reflect the differences within a given type of installations that result in variations in the environmental performances achieved when applying BAT. For example, a given BAT will not deliver the same performance for different installations, some BATs may not be suitable for use in certain installations, or a combination of BATs may be more effective on some pollutants or environmental media than others. The achievement of a high level of protection of human health and the environment as a whole has been jeopardised by the practice of setting emission limit values at the laxest end of the range of emission levels associated with the best available techniques, without considering the potential of a given installation to achieve lower emission levels through the application of best available techniques. Such practice discourages frontrunners from implementing more effective techniques, and hinders the achievement of a level-playing field at a high level of protection of human health and the environment. Competent authorities should therefore be required to set in permits the lowest possible emission limit values which reflect the performance of BAT for the specific installations, taking into consideration the whole range of BAT-AELs and aiming at the best environmental performance possible for the installations; unless the operator demonstrates that applying best available techniques as described in the BAT conclusions only allows the concerned installation to meeting less strict emission limit values. (16)The contribution of Directive 2010/75/EU to resource and energy efficiency and circular economy in the Union should be made more effective, taking into consideration the ‘Energy Efficiency First’ as a guiding principle of the Union energy policy. Therefore, the permits should establish, where possible, mandatory environmental performance limit values on consumption and resource efficiency levels, including on the use of water, energy and recycled materials, based on the environmental performance levels associated with the best available techniques (BAT AEPLs) set out in decisions on BAT conclusions. (17)With a view to preventing or minimising the emission of pollutants by installations within the scope of Directive 2010/75/EU and to levelling the playing field across the Union, the conditions under which derogations from emissions limit values can be granted should be better framed through general principles, in order to ensure a more harmonized implementation of such derogations throughout the Union. Moreover, derogations from emissions limit values should not be granted where they may put at risk compliance with environmental quality standards. (18)The evaluation of Directive 2010/75/EU concluded that there was some discrepancy in compliance assessment approaches for installations covered by Chapter II of that Directive. In order to achieve a high level of protection of the environment as a whole, ensure a consistent implementation of Union law and a level-playing field throughout the Union, while minimising the administrative burden on businesses and public authorities, the Commission should set common rules for assessing compliance with emission limit values and validation of measured levels for both air and water emissions based on best available techniques. Those compliance assessment rules should take precedent over the rules set out in Chapters III and IV on assessment of compliance with emission limit values contained in Annexes V and VI to Directive 2010/75/EU. (19)Environmental quality standards refer to all the requirements set out in Union law, such as Union legislation on air and water; which must be fulfilled at a given time by a given environment or particular part thereof. Therefore it is appropriate to clarify that when granting a permit to an installation, competent authorities should not only set out conditions to ensure compliance of the installation’s operations with the best available techniques conclusions, but should also, where appropriate with a view to reducing the specific contribution of the installation to the pollution occurring in the relevant area, include specific additional conditions in the permit stricter than those set in relevant BAT conclusions, so as to ensure the installation’s compliance with environmental quality standards. Such conditions may consist in setting stricter emission limit values or limiting the operation or capacity of the installation. (20)Permit conditions should be regularly reviewed and, where necessary, updated by the competent authority to ensure compliance with relevant legislation. Such review or update should also take place where it is necessary for the installation to comply with an environmental quality standard, including in the case of a new or revised environmental 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, such as the river basin management plans under Directive 2000/60/EC of the European Parliament and of the Council. (21)Parties to the Aarhus Convention on Access to Information, Public Participation in Decision-making and Access to Justice in Environmental Matters, at their seventh Meeting session, endorsed the Convention’s Compliance Committee’s findings in case ACCC/C/2014/121, according to which, by putting in place a legal framework that does not envisage any possibility for public participation in relation to reconsiderations and updates under Article 21 (3), (4) and (5)(b) and (c) of Directive 2010/75/EU, the European Union fails to comply with article 6 (10) of the Convention. These findings have been endorsed by the Union and its Member States, and with a view to reaching full compliance with the Aarhus Convention, it is necessary to specify that the public concerned should be given early and effective opportunities to participate in the granting or updating of permit conditions set by the competent authority also when permits conditions are reconsidered following the publication of decisions on BAT conclusions relating to the main activity of the installation; when developments in the best available techniques allow for the significant reduction of emissions; when the operational safety requires other techniques to be used; and where it is necessary to comply with a new or revised environmental quality standard. (22)As clarified by the case-law of the Court of Justice, Member States may not restrict legal standing to challenge a decision of a public authority to those members of the public concerned who participated in the preceding administrative procedure to adopt that decision. As also clarified by the case-law of the Court of Justice, effective access to justice in environmental matters and effective remedies requires inter alia that members of the public concerned should have the right to ask the court or ancompetent independent and impartial body to order interim measures to prevent a given instance of pollution, including, where necessary, through the temporary suspension of the disputed permit. Therefore, it should be specified that legal standing should not be made conditional on the role that the concerned member of the public played during a participatory phase of the decision-making procedures under this Directive. In addition, any review procedure should be fair, equitable, timely and not prohibitively expensive, and provide for adequate and effective redress mechanisms, including injunctive relief as appropriate. (23)Transboundary cooperation should take place prior to the granting of permits where more than one Member State may be affected by the operation of an installation, and should include prior information and consultation of the public concerned and competent authorities in the other Member States which may be affected. (24)The evaluation of Directive 2010/75/EU found that, even if it should foster the transformation of European industry, it is not dynamic enough and does not sufficiently support the deployment of innovative processes and technologies. It is therefore appropriate to facilitate the testing and deployment of emerging techniques with improved environmental performance, to facilitate cooperation with researchers and industries in publicly funded research projects subject to the conditions foreseen in the relevant European and national funding instruments, as well as to set up a dedicated centre to support innovation by collecting and analysing information on innovative techniques, including emerging techniques, relevant to activities within the scope of that Directive and to characterise their level of development from research to deployment (technology readiness level or ‘TRL’) and their environmental performance. This will also inform the exchange of information on drawing up, reviewing and updating BAT reference documents. Innovative techniques to be collected and analysed by the centre should be at least at the level of technology demonstrated in relevant environment (industrially relevant environment in the case of key enabling technologies) or system prototype demonstration in operation environment (TRL 6-7).

(25)Achieving Union objectives regarding a clean, circular and climate neutral economy by 2050 calls for a deep transformation of the Union economy. Consistently with the 8th Environmental Action Programme, operators of installations covered by Directive 2010/75/EU should therefore be required to include transformation plans in their environmental management systems. Such transformation plans will also complement the Corporate Sustainability Reporting requirements under Directive 2013/34/EU of the European Parliament and of the Council by providing a means for concrete implementation of these requirements at installation level. The first priority is the transformation of energy-intensive activities listed in Annex I. Therefore, the operators of energy-intensive installations should produce transformation plans by 30 June 2030. Operators of installations carrying out other activities listed in Annex I should be required to produce transformation plans as part of the permit reconsideration and update following the publication of decisions on BAT conclusions published after 1 January 2030. Whilst the transformation plans should remain indicative documents prepared under the responsibility of the operators, the audit organisation contracted by the operators as part of their environmental management systems should check that they contain the minimum information to be set by the European Commission in an implementing act, and the operators should make the transformation plans public. (26)Further clarity is needed regarding the criteria to assess whether the cleaned gases or liquids resulting from the gasification and pyrolysis of waste are sufficiently purified to such an extent that they are no longer waste prior to their incineration. (27)In light of the high number of rearing installations that should be included within the scope of Directive 2010/75/EU, and the relative simplicity of the processes and emissions patterns of such installations, it is appropriate to set out specific administrative procedures for issuing permits and for the operation of the relevant activities which are adapted to the sector, without prejudice to requirements related to public information and participation, montoring and compliance. (28)Innovative techniques coming on the market are expected to increasingly reduce both emissions of pollutants and of greenhouse gases from installations within the scope of both Directive 2010/75/EU and Directive 2003/87/EC of the European Parliament and of the Council. Whilst this will allow for the building of further synergies between those Directives, it may affect their operation, including on the carbon market. Directive 2003/87/EC contains in this regard a provision to review the effectiveness of synergies with Directive 2010/75/EU, and calling for environmental and climate relevant permits to be coordinated to ensure efficient and speedier execution of measures needed to comply with Union climate and energy objectives. In order to take into account the dynamics of innovation in this regard and the review referred to in Article 8 of Directive 2003/87/EC, the Commission should submit a report reviewing the implementation of Directive 2010/75/EU to the European Parliament and to the Council by 2028 and every 5 years thereafter. (29)In order to ensure that Directive 2010/75/EU continues meeting its objectives to prevent or reduce emissions of pollutants and achieve a high level of protection of human health and the environment, the power to adopt acts in accordance with Article 290 TFEU should be delegated to the Commission to supplement that Directive in order to establish operating rules containing requirements for activities relating to rearing of poultry, pigs and cattle, and to amend Annexes I and Ia to that Directive by adding an agro-industrial activity to ensure that it meets its objectives to prevent or reduce pollutants emissions and achieve a high level of protection of human health and the environment. It is of particular importance that the Commission carry out appropriate consultations during its preparatory work, including at expert level, and that those consultations be conducted in accordance with the principles laid down in the Interinstitutional Agreement on Better Law-Making of 13 April 2016. In particular, to ensure equal participation in the preparation of delegated acts, the European Parliament and the Council receive all documents at the same time as Member States' experts, and their experts systematically have access to meetings of Commission expert groups dealing with the preparation of delegated acts. (30)In order to ensure uniform conditions for the implementation of Directive 2010/75/EU, implementing powers should be conferred on the Commission as regards the establishment of (i) the format to be used for the permit summary; (ii) a standardised methodology for assessing the disproportionality between the costs of implementation of the BAT conclusions and the potential environmental benefits, (iii) the measuring method for assessing compliance with emission limit values set out in the permit with regard to emissions to air and water, (iv) the detailed arrangements necessary for the establishment and functioning of the innovation centre for industrial transformation and emissions, and (v) the format to be used for transformation plans. Those powers should be exercised in accordance with Regulation (EU) No 182/2011 of the European Parliament and of the Council. (31)In order to ensure the effective implementation and enforcement of the obligations set out in Directive 2010/75/EU, it is necessary to specify the minimum content of effective, proportionate and dissuasive penalties. Disparities in penalties regimes, the fact that imposed penalties are deemed in many cases too low to truly have a deterrent effect on illegal behaviours, and the lack of uniform implementation across Member States, undermine the level playing field on industrial emissions throughout the Union. Account should be taken of Directive 2008/99/EC on the protection of the environment through criminal law where a detected infringement under this Directive constitutes an offence within the scope Directive 2008/99/EC. (32)Where damage to human health has occurred as a result of a violation of national measures adopted pursuant to Directive 2010/75/EU, Member States should ensure that the individuals affected are able to claim and obtain compensation for that damage from the relevant natural or legal persons and, where appropriate, from the relevant competent authorities responsible for the infringement. Such rules on compensation contribute to pursuing the objectives of preserving, protecting and improving the quality of the environment and protecting human health as laid down in Article 191 TFEU. They also underpin the right to life, integrity of the person and health care laid down in Article 2, 3 and 35 of the Charter of Fundamental Rights of the European Union and the right to an effective remedy as laid down in Article 47 of the Charter. Moreover, Directive 2004/35/EC of the European Parliament and of the Council does not give private parties a right of compensation as a consequence of environmental damage or of an imminent threat of such damage. (33)It is therefore appropriate for Directive 2010/75/EU to address the right for compensation for damages suffered by individuals. To ensure that individuals can defend their rights against damages to health caused by violations of Directive 2010/75/EU and thereby ensure a more efficient enforcement of that Directive, non-governmental organisations promoting the protection of human health or the environment, including those promoting the protection of consumers and meeting any requirements under national law, as members of the public concerned, should be empowered to engage in proceedings, as the Member States so determine, either on behalf or or in support of any victim, without prejudice to national rules of procedure concerning representation and defence before the courts. Member States usually enjoy procedural autonomy to ensure an effective remedy against violations of Union law, subject to the respect of the principles of equivalence and effectivity. However, experience shows that while there is overwhelming epidemiologic evidence on the negative health impacts of pollution on the population, in particular as regards air, it is difficult for the victims of violations of Directive 2010/75/EU under the procedural rules on the burden of proof generally applicable in the Member States to demonstrate a causality link between the suffered harm and the violation. As a result, in the majority of cases, victims of violations of Directive 2010/75/EU do not have an effective way to obtain compensation for the harm caused by such violations. To strengthen the rights of individuals to obtain compensation for violations of Directive 2010/75/EU and to contribute to a more efficient enforcement of its requirements throughout the Union, it is necessary to adapt the burden of proof applicable to such situations. Therefore, when an individual can provide sufficiently robust evidence to give rise to a presumption that the violation of Directive 2010/75/EU is at the origins of the damage caused to the health of an individual, or has significantly contributed to it, it should be for the defendant to rebut that presumption in order to escape his liability. (34)The impact of Directive 2010/75/EU on the procedural autonomy of the Member States should be limited to what is necessary to ensure the objectives of protection of human health through a safe environment pursued by it and should not affect other national procedural rules establishing the right to seek compensation for violations of that Directive. Such national rules should however not hamper the effective functioning of the mechanism for seeking compensation required by Directive 2010/75/EU. (35)The implementation of Directive 2010/75/EU has shown divergent applications across Member States concerning the coverage of installations for the manufacturing of ceramic products by firing, because the wording of the definition of this activity allowed Member States to decide whether to apply both or only one of the two criteria on production capacity and kiln capacity. With a view to ensuring a more consistent implementation of that Directive and securing a level-playing field throughout the Union, such installations should be included within the scope of that Directive whenever any one of those two criteria is met. (36)When setting emission limit values for polluting substances, the competent authority should consider all substances, including substances of emerging concern, which may be emitted from the concerned installation and may have a significant impact on the environment or human health. In doing so, the hazard characteristics, quantity and nature of the substances emitted and their potential to pollute any environmental media should be considered. The BAT conclusions, where relevant, are the reference point for selecting the substances for which emission limit values are to be set, although the competent authority may decide to select additional substances. Currently, individual polluting substances are listed in a non-exhaustive way in Annex II to Directive 2010/75/EU; which is not compatible with the holistic approach of that Directive and does not reflect the need for competent authorities to take into account all relevant polluting substances, including those of emerging concern. The non-exhaustive list of polluting substances should therefore be deleted. Instead, reference should be made to the list of pollutants in Annex II to Regulation (EC) No 166/2006. (37)Although landfills are included within the scope of Directive 2010/75/EU, no BAT conclusions exist for landfills since that activity falls within the scope of Council Directive 1999/31/EC and the requirements of the latter Directive are deemed to constitute BAT. Due to the technical developments and innovation that have taken place since the adoption of Directive 1999/31/EC, more effective techniques for protecting human health and the environment are now available. The adoption of BAT conclusions under Directive 2010/75/EU would allow addressing the key environmental issues related to the operation of waste landfills, including significant emissions of methane. Directive 1999/31/EC should therefore allow for the adoption of BAT conclusions on landfills under Directive 2010/75/EU. (38)Directives 2010/75/EU and 1999/31/EC should therefore be amended accordingly. (39)Since the objectives of this Directive, namely to ensure a high level of environmental protection and the improvement of environmental quality, cannot be sufficiently achieved by Member States and can, therefore, by reason of the transboundary nature of pollution from industrial activities, be better achieved at Union level, the Union may adopt measures in accordance with the principle of subsidiarity as set out in Article 5 of the Treaty on European Union. In accordance with the principle of proportionality, as set out in that Article, this Directive does not go beyond what is necessary in order to achieve those objectives. (40)In accordance with the principle of proportionality, it is necessary and appropriate for the achievement of the basic objective of ensuring a high level of environmental protection and the improvement of environmental quality to lay down rules on integrated prevention and control of pollution arising from industrial activities. This Directive does not go beyond what is necessary in order to achieve the objectives pursued, in accordance with Article 5(4) of the Treaty on European Union. (41)In accordance with the Joint Political Declaration of 28 September 2011 of Member States and the Commission on explanatory documents, Member States have undertaken to accompany, in justified cases, the notification of their transposition measures with one or more documents explaining the relationship between the components of a directive and the corresponding parts of national transposition instruments. With regard to this Directive, the legislator considers the transmission of such documents to be justified, HAVE ADOPTED THIS DIRECTIVE: Article 1 Amendments to Directive 2010/75/EU

Directive 2010/75/EU is amended as follows: (1) In Article 1, the second paragraph is replaced by the following: ‘It also lays down rules designed to prevent or, where that is not practicable, to reduce emissions into air, water and land and to prevent the generation of waste, in order to achieve a high level of protection of human health and the environment taken as a whole.’. (2) In Article 2, paragraph 1 is replaced by the following: ‘1. This Directive shall apply to the industrial activities giving rise to pollution referred to in Chapters II to VIa.’. (3) Article 3 is amended as follows: (a)point (3) is replaced by the following: ‘(3) ‘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;’; (b)point (12) is replaced by the following: ‘(12) ‘BAT conclusions’ means a document containing the parts of a BAT reference document laying down the conclusions on best available techniques, their description, information to assess their applicability, the emission levels associated with the best available techniques, the environmental performance levels associated with the best available techniques, the minimum content of an environmental management system including benchmarks associated with the best available techniques, associated monitoring, associated consumption levels and, where appropriate, relevant site remediation measures;’; (c)the following point (13a) is inserted: ‘(13a) ‘environmental performance levels associated with the best available techniques’ means the range of environmental performance levels, except emission levels, obtained under normal operating conditions using a BAT or a combination of BATs;’. (d)point (17) is replaced by the following: ‘(17) ‘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;’. (e)the following points (23a), (23b) and (23c) are inserted: ‘(23a) ‘pigs’ means pigs as defined in Article 2 of Council Directive 2008/120/EC*; (23b) ‘cattle’ means domestic animals of the species Bos taurus; (23c) ‘livestock unit’ or ‘LSU’ means the grazing equivalent of one adult dairy cow producing 3 000 kg of milk annually, without additional concentrated foodstuffs, which is used to express the size of farms rearing different categories of animals, using the conversion rates, with reference to actual production within the calendar year, set out in Annex II to Commission Implementing Regulation (EU) No 808/2014**’.

* Council Directive 2008/120/EC of 18 December 2008 laying down minimum standards for the protection of pigs (OJ L 47, 18.2.2009, p. 5). ** Commission Implementing Regulation (EU) No 808/2014 of 17 July 2014 laying down rules for the application of Regulation (EU) No 1305/2013 of the European Parliament and of the Council on support for rural development by the European Agricultural Fund for Rural Development (EAFRD) (OJ L 227 31.7.2014, p. 18).’;. (f)the following points (48) to (53) are added: ‘(48) ‘industrial minerals’ means minerals used in industry for the production of semi-finished or finished products, with the exception of metalliferous ores, energy minerals, construction minerals and precious stones; (49) ‘metalliferous ores’ means ores that yield metals or metallic substances; (50) ‘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, expressed as an average over a given period of time, under specified reference conditions; (51) ‘environmental performance levels associated with emerging techniques’ means the range of environmental performance levels, except emission levels, obtained under normal operating conditions using an emerging technique or a combination of emerging techniques; (52) ‘compliance assurance’ means mechanisms for securing compliance using three categories of intervention: compliance promotion; compliance monitoring; follow-up and enforcement.’; (53) ‘‘benchmarks’ means the indicative range of environmental performance levels associated with best available techniques, other than emission levels, and may include: (a) consumption levels; (b) resource efficiency levels and reuse levels covering materials, water and energy resources; (e) waste and other levels obtained under specified reference conditions.’. (4) In Article 4(1), the second subparagraph is replaced by the following: ‘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.’. (5) In Article 5, the following paragraph (4) is added: ‘4. Member States shall ensure that permits granted pursuant to this Article are made available on the Internet, free of charge and without restricting access to registered users. In addition, a summary of each permit shall be made available to the public under the same condtions. That summary shall include at least the following: (a) an overview of the main permit conditions; (b) the emission limit values and environmental performance limits values; (c) any derogations granted in accordance with Article 15(4);

(d) the applicable BAT conclusions; (e) the provisions for reconsideration and updating of the permit. The Commission shall adopt an implementing act to establish the format to be used for the summary referred to in the second subparagraph. That implementing act shall be adopted in accordance with the examination procedure referred to in Article 75(2).’. (6) Articles 7 and 8 are replaced by the following: ‘Article 7 Incidents and accidents Without prejudice to Directive 2004/35/EC of the European Parliament and of the Council*, 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: (a) the operator informs the competent authority immediately; (b) the operator immediately takes the measures to limit the environmental consequences and to prevent further possible incidents or accidents; (c) the competent authority requires the operator to take any appropriate complementary measures that the competent authority considers necessary to limit the environmental consequences and to prevent further possible incidents or accidents. 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 aim at limiting the consequences on the environment and human health and to prevent further possible incidents or accidents. Article 8 Non-compliance 1.Member States shall take the necessary measures to ensure that the permit conditions are complied with. They shall also adopt compliance assurance measures to to promote, monitor and enforce compliance with obligations placed on natural or legal persons under this Directive. 2.In the event of a breach of the permit conditions, Member States shall ensure that: (a) the operator immediately informs the competent authority; (b) the operator immediately takes the measures necessary to ensure that compliance is restored within the shortest possible time; (c) the competent authority requires the operator to take any appropriate complementary measures that the competent authority considers necessary to restore compliance.

Where the breach of the permit conditions poses an immediate danger to human health or threatens to cause an immediate significant adverse effect upon the environment, and until compliance is restored in accordance with the first subparagraph, points (b) and (c), the operation of the installation, combustion plant, waste incineration plant, waste co-incineration plant or relevant part thereof shall be suspended without any delay. 3.Where the breach of the permit conditions continues to cause a danger to human health or a a significant adverse effect upon the environment, and where the necessary action for restoring comp