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Official Journal EN
of the European Union L series
2026/805 20.4.2026
DIRECTIVE (EU) 2026/805 OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL
of 30 March 2026
amending Directive 2000/60/EC establishing a framework for Community action in the field of water
policy, Directive 2006/118/EC on the protection of groundwater against pollution and deterioration
and Directive 2008/105/EC on environmental quality standards in the field of water policy
(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(1),
After consulting the Committee of the Regions,
Acting in accordance with the ordinary legislative procedure(2),
Whereas:
(1) On 28 July 2010, the United Nations General Assembly recognised the right to safe and clean drinking water and
sanitation as a human right that is essential for the full enjoyment of life and all human rights. To fully realise that
right in the Union, Member States should improve access to clean water and sanitation, in particular by improving
the quality of both surface water and groundwater used for the abstraction of drinking water by implementing
Directive 2000/60/EC(3), and through the effective implementation of Directives (EU) 2020/2184(4) and (EU)
2024/3019(5) of the European Parliament and of the Council.
(2) Chemical pollution of surface water and groundwater poses a threat to the aquatic environment, with effects such as
acute and chronic toxicity in aquatic organisms, accumulation of pollutants in the ecosystem and loss of habitats and
biodiversity, as well as to human health. Setting environmental quality standards helps to implement the
zero-pollution ambition for a toxic-free environment.
(3) According to the European Environment Agency’s report entitled ‘Europe’s state of water 2024’, in 2021 Member
States reported that around 90 % of the area of groundwater bodies was in good quantitative status, and around
75 % was in good chemical status, while 40 % of surface water bodies were in good or high ecological status, and
38 % in good chemical status. As outlined in the Commission’s 7th Implementation Report (2024), assessing the
third river basin management plans, the reasons for this are manifold. As regards chemical status, some positive
trends are masked by historic, widespread contamination by mercury and other ubiquitous, bioaccumulative and
toxic pollutants or are overshadowed by new, emerging pollution challenges. As regards ecological status, there has
been some improvement in certain biological quality elements. However, rivers, lakes and coastal waters in the
Union are still subject to significant pressures and, even when effective measures are taken, progress may not be
visible over the short term in the monitoring results because nature needs sufficient time to recover.
(1) Opinion of 22 February 2023 (OJ C 146, 27.4.2023, p. 41).
(2) Position of the European Parliament of 24 April 2024 (not yet published in the Official Journal) and position of the Council at first
reading of 17 February 2026 (not yet published in the Official Journal).
(3) Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community
action in the field of water policy (OJ L 327, 22.12.2000, p. 1, ELI: http://data.europa.eu/eli/dir/2000/60/oj).
(4) Directive (EU) 2020/2184 of the European Parliament and of the Council of 16 December 2020 on the quality of water intended for
human consumption (OJ L 435, 23.12.2020, p. 1, ELI: http://data.europa.eu/eli/dir/2020/2184/oj).
(5) Directive (EU) 2024/3019 of the European Parliament and of the Council of 27 November 2024 concerning urban wastewater
treatment (OJ L, 2024/3019, 12.12.2024, ELI: http://data.europa.eu/eli/dir/2024/3019/oj).
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(4) Overall, the conclusions of the 2019 Fitness Check of Directives 2000/60/EC, 2006/118/EC(6), 2007/60/EC(7)and
2008/105/EC(8)of the European Parliament and of the Council (the ‘Fitness Check’) indicate that those Directives are
broadly fit for purpose, with some scope for improvement. The conclusions indicate that those Directives have so far
generally led to a higher level of protection of water bodies and better flood risk management. However, they also
point out that currently more than half of all European water bodies are subject to exemptions under Directive
2000/60/EC, which indicates that Member States face a very substantial challenge to achieve the objective of good
water status, and in particular to comply with the environmental quality standards (EQS) for priority substances,
within the given deadlines. In addition, the Fitness Check concluded that the slow progress made as regards
achieving the objectives of those Directives can, amongst other things, be attributed to slow implementation, in part
due to a lack of sufficient financial resources as well as insufficient integration of environmental objectives into
sectoral legislation.
(5) As reported in the Commission assessment of 4 February 2025 on the implementation of Directive 2000/60/EC
based on the Member States’ third river basin management plans, the Union’s water resources remain under severe
pressure due to structural mismanagement, unsustainable land use, hydro-morphological changes, pollution, climate
change, increased demand for water and urbanisation. The most significant pressures on surface water bodies in all
reporting Member States are, in descending order of the percentage of water bodies affected: pollution from
atmospheric deposition, hydro-morphological changes stemming from drainage and irrigation for agriculture,
hydropower, flood protection, navigation or drinking water supply, and pollution from agriculture. Similarly, the
biggest pressures on groundwater bodies are, first, diffuse agricultural pollution, for example from the use of
pesticides and fertilisers, and second, in descending order, abstraction for public water supply, for agriculture, for
industrial use and for other purposes. Addressing those combined pressures is essential to ensure the sustainable
management and protection of water bodies. This requires integrated approaches that promote the reduction of
pollution at source and the remediation of existing pollution, the restoration of ecosystems, the adoption of efficient
water-use technologies, and the implementation of sustainable practices across sectors. Member States should
strengthen the coordination between water and sectorial policies to reduce negative impacts on water resources and
support the achievement of good ecological, quantitative and chemical status as set out in Directive 2000/60/EC.
(6) Pursuant to Article 191(2) of the Treaty on the Functioning of the European Union (TFEU), Union policy on the
environment is to be based on the precautionary principle and on the principles that preventive action is to be taken,
that environmental damage is, as a priority, to be rectified at source and that the polluter is to pay.
(7) In seeking to achieve a high level of environmental protection and in implementing the Zero Pollution Action Plan
set out in the communication of the Commission of 12 May 2021 on the Pathway to a Healthy Planet for All – EU
Action Plan: ‘Towards Zero Pollution for Air, Water and Soil’, the Union should take account of the diversity of
situations in the different regions of the Union, the impact on food security, food production and food affordability,
as well as healthy and sustainable diets.
(6) Directive 2006/118/EC of the European Parliament and of the Council of 12 December 2006 on the prevention and control of
groundwater pollution (OJ L 372, 27.12.2006, p. 19, ELI: http://data.europa.eu/eli/dir/2006/118/oj).
(7) Directive 2007/60/EC of the European Parliament and of the Council of 23 October 2007 on the assessment and management of
flood risks (OJ L 288, 6.11.2007, p. 27, ELI: http://data.europa.eu/eli/dir/2007/60/oj).
(8) Directive 2008/105/EC of the European Parliament and of the Council of 16 December 2008 on environmental quality standards
and on the prevention and control of surface water pollution, amending and subsequently repealing Council Directives 82/176/EEC,
83/513/EEC, 84/156/EEC, 84/491/EEC, 86/280/EEC and amending Directive 2000/60/EC of the European Parliament and of the
Council (OJ L 348, 24.12.2008, p. 84, ELI: http://data.europa.eu/eli/dir/2008/105/oj).
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(8) The Commission’s communication of 11 December 2019 on the European Green Deal sets out a strategy to ensure,
by 2050, a climate-neutral, clean and circular economy, optimising resource management while minimising
pollution. The communication of the Commission of 14 October 2020 on the Chemicals Strategy for Sustainability
Towards a Toxic-Free Environment and the Zero Pollution Action Plan specifically address pollution aspects of the
European Green Deal. Other particularly relevant and complementary policies are set out in the communications of
the Commission of 16 January 2018 on a European Strategy for Plastics in a Circular Economy, of 19 February 2020
on Shaping Europe’s digital future, of 19 February 2020 on a European strategy for data, of 20 May 2020 on a Farm
to Fork Strategy for a fair, healthy and environmentally-friendly food system, of 20 May 2020 on the EU Biodiversity
Strategy for 2030 Bringing nature back into our lives, of 25 November 2020 on the Pharmaceutical Strategy for
Europe, of 17 November 2021 on the EU Soil Strategy for 2030 Reaping the benefits of healthy soils for people,
food, nature and climate and of 4 June 2025 on the European Water Resilience Strategy.
(9) The objectives of achieving ‘good status of water bodies’ and of ensuring water availability are cross-cutting and are
often not pursued in a sufficiently coherent way. Sustainable water management should be mainstreamed across all
Union policies concerning water-using sectors.
(10) Directive 2000/60/EC establishes a framework for the protection of inland surface waters, transitional waters,
coastal waters and groundwater. That framework involves the identification of priority substances amongst those
that pose a significant risk to or via the aquatic environment at Union level. Directive 2008/105/EC lays down
Union-wide EQS for the 45 priority substances previously listed in Annex X to Directive 2000/60/EC and eight
other pollutants that were already regulated at Union level before that Annex was introduced by Decision
No 2455/2001/EC of the European Parliament and of the Council(9). Directive 2006/118/EC lays down Union-wide
groundwater quality standards for nitrates and for active substances in pesticides and criteria for establishing
national threshold values for other groundwater pollutants. It also sets out a minimum list of 12 pollutants and
indicators of pollution for which Member States are required to consider establishing such national threshold values.
The groundwater quality standards are set out in Annex I to Directive 2006/118/EC.
(11) It should be ensured that the discharges, emissions and losses of priority hazardous substances cease or are phased
out within an appropriate timeline and, in any case, not later than 20 years after a given priority substance is listed as
hazardous in Part A of Annex I to Directive 2008/105/EC. That timeline should apply without prejudice to the
application of stricter timelines in any other applicable Union legislation.
(12) Substances are considered for listing in Part A of Annex I to Directive 2008/105/EC or in Annex I or Part B of
Annex II to Directive 2006/118/EC based on an assessment of the risk they pose to humans and the aquatic
environment. The key components of that assessment are knowledge of the environmental concentrations of the
substances, including information collected from watch-list monitoring, and the (eco)toxicity of the substances, as
well as their persistence, bioaccumulation, mobility, carcinogenicity, mutagenicity, reprotoxicity and endocrine-
disrupting potential.
(13) The Commission has conducted a review of the list of priority substances previously in Annex X to Directive
2000/60/EC in accordance with Article 16 thereof and with Article 8 of Directive 2008/105/EC, and a review of the
lists of substances in Annex I and Part B of Annex II to Directive 2006/118/EC in accordance with Article 10 thereof
and has concluded, in the light of new scientific knowledge, that it is appropriate to amend those lists by adding new
substances, setting EQS or groundwater quality standards for those newly added substances, revising the EQS for
some existing substances in line with scientific progress and setting biota or sediment EQS for some existing and
newly added substances. The Commission has also identified which additional substances are likely to accumulate in
sediment or biota, and clarified that trend monitoring of such substances should be conducted in sediment or biota.
The reviews of the lists of substances have been supported by an extensive consultation with experts from the
Commission services, Member States, stakeholder groups and the Scientific Committee on Health, Environmental
and Emerging Risks.
(9) Decision No 2455/2001/EC of the European Parliament and of the Council of 20 November 2001 establishing the list of priority
substances in the field of water policy and amending Directive 2000/60/EC (OJ L 331, 15.12.2001, p. 1, ELI: http://data.europa.eu/
eli/dec/2001/2455/oj).
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(14) A combination of source-control and end-of-pipe measures is required to effectively deal with most pollutants across
their life cycle, including, as relevant, chemical design, authorisation or approval, control of emissions during
manufacturing and use or other processes, and waste handling. The setting of new or stricter quality standards in
water bodies therefore complements and is coherent with other Union legislation that addresses or could address the
pollution problem at one or more of those stages, including Directive 2001/83/EC of the European Parliament and
of the Council(10), Regulations (EC) No 1907/2006(11)and (EC) No 1107/2009(12)of the European Parliament and
of the Council, Directives 2009/128/EC(13) and 2010/75/EU(14) of the European Parliament and of the Council,
Regulations (EU) No 528/2012(15)and (EU) 2019/6(16)of the European Parliament and of the Council and Directive
(EU) 2024/3019. In order to achieve the environmental objectives laid down in Article 4 of Directive 2000/60/EC in
the most cost-effective way possible, the Commission and the Member States should prioritise, where possible, in
their actions and programmes of measures, respectively, source-control measures, as well as their enforcement.
Coherence between all pieces of Union and national legislation addressing pollutant emissions at source should be
ensured in order to reduce pollution to levels no longer considered harmful to health and natural ecosystems.
(15) New scientific evidence points to a significant risk from several other pollutants found in water bodies, in addition to
those already regulated. In groundwater, a particular problem has been identified through voluntary monitoring for
per- and polyfluoroalkyl substances (PFAS) and pharmaceuticals. PFAS have been detected at more than 70 % of the
groundwater measuring points in the Union and existing national threshold values are clearly exceeded at
a considerable number of locations. A subset of specific PFAS should therefore be added to the list of groundwater
pollutants. In surface waters, perfluorooctane sulfonic acid (PFOS) and its derivatives are already listed as priority
substances, but other PFAS are now also recognised as posing a risk. A subset of specific PFAS should therefore be
added to the list of priority substances. Voluntary monitoring in groundwater and watch-list monitoring under
Article 8b of Directive 2008/105/EC have also confirmed a risk in groundwaters and surface waters from a number
of pharmaceutical substances which should therefore be added, as relevant, to the list of pollutants in Annex I to
Directive 2006/118/EC or to the priority substances list in Annex I to Directive 2008/105/EC. In groundwater, the
Commission should consider addressing the cumulative risk from pharmaceuticals, by setting quality standards for
the sum(s) of selected pharmaceuticals, potentially based on mode of action, at the next review. For that reason, ‘sum
(s) of selected pharmaceuticals by mode of action’ should be added to Annex V to Directive 2006/118/EC. In surface
water, the cumulative risk from estrogenic pharmaceuticals should be addressed by effect-based monitoring and,
taking into account data from more recent and ongoing watch-list monitoring, the Commission should consider
setting standards for the sum(s) of selected pharmaceuticals, potentially based on mode of action, at the next review;
for that reason ‘sum(s) of selected pharmaceuticals by mode of action’ should be added to Annex III to Directive
2008/105/EC. The Commission should also consider setting standards for total pharmaceuticals, supported by
appropriate monitoring methods. Member States are encouraged to monitor also the totality of PFAS (‘PFAS Total’) in
groundwater using the guidance adopted under Article 13(7) of Directive (EU) 2020/2184. The Commission should
consider the guidance and the results obtained by Member States in defining a monitoring method for PFAS Total
specifically in groundwater and encourage Member States to apply it. The Commission should adapt that monitoring
method to facilitate the monitoring of PFAS Total in surface water and encourage the Member States to apply it. The
Commission should also consider setting quality standards for PFAS Total in groundwater and surface waters during
the next review of the lists of pollutants set out in Annex I to Directives 2006/118/EC and Annex I to Directive
2008/105/EC.
(10) Directive 2001/83/EC of the European Parliament and of the Council of 6 November 2001 on the Community code relating to
medicinal products for human use (OJ L 311, 28.11.2001, p. 67, ELI: http://data.europa.eu/eli/dir/2001/83/oj).
(11) Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006 concerning the Registration,
Evaluation, Authorisation and Restriction of Chemicals (REACH), establishing a European Chemicals Agency, amending Directive
1999/45/EC and repealing Council Regulation (EEC) No 793/93 and Commission Regulation (EC) No 1488/94 as well as Council
Directive 76/769/EEC and Commission Directives 91/155/EEC, 93/67/EEC, 93/105/EC and 2000/21/EC (OJ L 396, 30.12.2006,
p. 1, ELI: http://data.europa.eu/eli/reg/2006/1907/oj).
(12) Regulation (EC) No 1107/2009 of the European Parliament and of the Council of 21 October 2009 concerning the placing of plant
protection products on the market and repealing Council Directives 79/117/EEC and 91/414/EEC (OJ L 309, 24.11.2009, p. 1,
ELI: http://data.europa.eu/eli/reg/2009/1107/oj).
(13) Directive 2009/128/EC of the European Parliament and of the Council of 21 October 2009 establishing a framework for
Community action to achieve the sustainable use of pesticides, (OJ L 309, 24.11.2009, p. 71, ELI: http://data.europa.eu/eli/dir/2009/
128/oj).
(14) Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial and livestock rearing
emissions (integrated pollution prevention and control) (OJ L 334, 17.12.2010, p. 17, ELI: http://data.europa.eu/eli/dir/2010/75/oj).
(15) Regulation (EU) No 528/2012 of the European Parliament and of the Council of 22 May 2012 concerning the making available on
the market and use of biocidal products (OJ L 167, 27.6.2012, p. 1, ELI: http://data.europa.eu/eli/reg/2012/528/oj).
(16) Regulation (EU) 2019/6 of the European Parliament and of the Council of 11 December 2018 on veterinary medicinal products and
repealing Directive 2001/82/EC (OJ L 4, 7.1.2019, p. 43, ELI: http://data.europa.eu/eli/reg/2019/6/oj).
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(16) Bisphenol-A should be added to the list of substances in Annex I to Directive 2008/105/EC and designated as
a priority hazardous substance. Scientific evidence shows that bisphenols other than Bisphenol-A have
endocrine-disrupting potential, and thus that replacing the use of one by the use of another might not have the
intended benefit. Further, mixtures of bisphenols could pose a cumulative risk. The Commission should therefore
review the listing of bisphenols in general at the next review, and consider the establishment of an EQS for the
totality of bisphenols (‘Bisphenols Total’) or at least for the sum of selected bisphenols (‘Sum of Bisphenols’),
including at least Bisphenol-B and Bisphenol-S, supported by appropriate monitoring methods. The ‘Sum of
Bisphenols’ should therefore be listed in Annex III to Directive 2008/105/EC. Furthermore, Member States should
give particular consideration to whether to identify and monitor at least Bisphenol B and Bisphenol S as river basin
specific pollutants, where potentially relevant, and to reporting the data in accordance with Article 8(4) of Directive
2000/60/EC to ensure that the risk from the sum of those bisphenols and Bisphenol A can be properly assessed at
the next review. The Commission should also consider establishing quality standards for ‘Bisphenols Total’ and ‘Sum
of Bisphenols’ in Directive 2006/118/EC.
(17) Taking into account that groundwater is the main source of drinking water in the Union, it is essential to ensure that
the quality standards set in Directive 2006/118/EC support the achievement of the parametric values set for
drinking water under Directive (EU) 2020/2184. Although it might be appropriate to harmonise the standards for
PFAS, it has recently been demonstrated that the parametric value relating to the sum of the 20 PFAS, as listed in Part
B, point 3, of Annex III to Directive (EU) 2020/2184, is not in line with the latest scientific developments with
respect to the list of PFAS to be given priority consideration, the toxicity of these substances and the variability of
toxicity between the substances in this family. In the absence of a complete and final agreement on PFAS standards,
a quality standard for the group of 20 PFAS, as listed in Part B, point 3, of Annex III to Directive (EU) 2020/2184, is
set out in Annex I of Directive 2006/118/EC, by way of reference to the parametric value for that group in Directive
(EU) 2020/2184 in order to ensure that any change to the composition of that group or that value be automatically
incorporated into Directive 2006/118/EC. To take account of the most recent scientific knowledge, a quality
standard for the sum of the four most problematic PFAS should be added to Annex I to Directive 2006/118/EC in
accordance with the value proposed by the European Food Safety Authority (EFSA). For the same reason, it is of
utmost importance that the parametric values for PFAS in Directive (EU) 2020/2184 be promptly reviewed and
revised as appropriate and, in such a case that the quality standards in Annex I to Directive 2006/118/EC also be
aligned.
(18) Considering the toxicity of trifluoroacetic acid (TFA), its persistence and prevalence in the environment, and its many
sources, including the use of PFAS pesticides and fluorine-containing refrigerant gases, it is extremely important to
address its presence in both surface water and groundwater. For surface water, TFA should therefore be included in
a sum of 25 PFAS with an EQS in Annex I to Directive 2008/105/EC. At the next review, the Commission should
consider establishing a separate EQS for TFA in Annex I to Directive 2008/105/EC. For groundwater, the
Commission should also consider establishing a quality standard for TFA, whether separate or as a part of a sum, in
Annex I to Directive 2006/118/EC, taking into account the most recent scientific knowledge on TFA, including work
carried out by the European Chemicals Agency (ECHA), EFSA and the World Health Organization (WHO). Future
amendments of Directive (EU) 2020/2184 should also be taken into account.
(19) There is a need to gather more knowledge about the presence, importance and sensitivity of groundwater ecosystems
in order to properly protect them. Additional scientific research should therefore be encouraged, funded and
conducted, and the findings should be disseminated, and, where necessary, taken into account, along with existing
knowledge, when implementing or revising Directives 2000/60/EC and 2006/118/EC. The Commission should
work with Member States under the Common Implementation Strategy for Directive 2000/60/EC to establish
a methodology for identifying groundwater ecosystems. As soon as a reliable methodology is available, Member
States should, where relevant, apply that methodology, and set stricter standards where necessary to protect those
ecosystems.
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(20) Directive 2000/60/EC requires Member States to identify water bodies used for the abstraction of water intended for
human consumption, to monitor them, and to take the necessary measures to avoid deterioration in their quality
and to reduce the level of purification treatment required in the production of water that is fit for human
consumption. In that context, micro-plastics have been identified as a potential risk to human health, but more
monitoring data are required to confirm the need for setting quality standards for micro-plastics in surface water and
groundwater. Micro-plastics should therefore be included in the surface water and groundwater watch lists and
should be monitored as soon as suitable monitoring methods are available. In that context, account should be taken
of the methodologies, developed under Directive (EU) 2020/2184, for monitoring and assessing the risks from
micro-plastics in drinking water.
(21) It is estimated that in 2019, between 900 000 and 1,7 million deaths around the world were attributable to
antimicrobial resistance (AMR) infections. At the same time, concern has been expressed about the risk of
antimicrobial resistance developing from the presence of antimicrobial resistant microorganisms and antimicrobial
resistance genes in the aquatic environment, but little monitoring has taken place. Appropriate indicators for the
presence, evolution or transmission of antimicrobial resistance should also be included in the surface water and
groundwater watch lists and monitored as soon as suitable monitoring methods have been developed. This is in line
with the ‘European One Health Action Plan against Antimicrobial Resistance’, adopted by the Commission in June
2017, and with the Commission communication of 25 November 2020 entitled ‘Pharmaceutical Strategy for
Europe’, which also addresses that concern.
(22) Directives 2006/118/EC and 2008/105/EC should each contain an annex listing selected substances, groups of
substances, and indicators to be considered by the Commission in the next review of those Directives, pending
development of reliable monitoring methodologies and appropriate quality standards or trigger values and final
confirmation that they pose a risk to or via groundwater or surface water. That confirmation could, if necessary, be
obtained by including the substances, groups of substances, or indicators in the relevant watch list.
(23) The conventional chemical analytical methods used for monitoring substances under Directives 2000/60/EC,
2006/118/EC and 2008/105/EC cannot, in general, determine the cumulative risk from mixtures of substances.
Considering the growing awareness of the relevance of mixtures and therefore of effect-based monitoring for
determining chemical status, and considering that sufficiently robust effect-based monitoring methods already exist
for estrogenic substances, Member States should apply such effect-based monitoring methods to assess the
cumulative effects of estrogenic substances in surface waters over a period of at least two years. This will allow the
comparison of effect-based results with the results obtained using the conventional methods for monitoring the
three estrogenic pharmaceutical substances listed in Annex I to Directive 2008/105/EC. For that purpose, the
Commission should adopt an implementing act setting out the technical specifications for the monitoring of
estrogenic substances using effect-based monitoring methods. The Commission should also publish a report on the
comparison of effect-based results with the results obtained using the conventional methods, and an analysis of it
should be used to assess whether effect-based monitoring methods deliver data that are robust and accurate enough
to allow those methods to be used as reliable screening methods. Using such screening methods would have the
advantage of allowing the effects of all estrogenic substances having similar effects to be covered, not only those
listed in Annex I to Directive 2008/105/EC, and could also replace substance-by-substance monitoring at many
locations. The concept of effect-based trigger values should be defined. The definition of good surface water
chemical status in Directive 2000/60/EC should be modified to ensure that it could, in the future, also cover trigger
values that might be set for assessing the results of effect-based monitoring.
(24) Whereas the risk from mixtures of pesticides is to some degree covered in Directive 2006/118/EC by the quality
standard for total pesticides, the risk from such mixtures is not addressed in Directive 2008/105/EC. To at least
partly address that cumulative risk, an EQS should therefore be set for the sum of the pesticides that are already
included in the list of priority substances that are to be monitored in water, and that EQS should be taken into
account when assessing chemical status. To take better account of mixture risk in the future, the Commission should
consider setting standards for the sum(s) of selected pesticides, potentially based on mode of action and possibly
covering more pesticides than those listed individually in Annex I to Directive 2008/105/EC, at the next review. For
that reason, the ‘sum(s) of selected pesticides by mode of action’ should be included in a new annex to that Directive.
The Commission should also consider whether a risk-based approach could be taken to establishing an EQS for total
pesticides, supported by an appropriate monitoring method. Because the generic quality standards of 0,1 μg/L and
0,5 μg/L for individual and total pesticides in groundwater specified in Annex I to Directive 2006/118/EC were
established in the 1980s, and limited by the sensitivity of the analytical methods available at that time, they may not
be sufficiently protective of human health or the environment. The Commission should therefore review those
values at the next review of the list of pollutants in groundwater.
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(25) As a result of its review of the list of substances in Part A of Annex I to Directive 2008/105/EC, the Commission
identified a number of substances that it could remove from the list because they no longer pose a widespread risk to
or via the aquatic environment within the Union. However, because those substances still pose a risk in some
Member States, it is appropriate to include them, with their EQS, in a new annex to Directive 2008/105/EC. Member
States should continue to monitor those substances if they identify them as pollutants of national, regional or local
concern, and to apply the EQS accordingly. Some other substances were considered for deselection but have been
retained in the list because of the need to determine whether their concentrations are showing a downward trend.
For some of them, monitoring under Directives 2000/60/EC and 2008/105/EC also contributes to fulfilling
monitoring obligations under the Stockholm Convention on persistent organic pollutants(17) (‘Stockholm
Convention’), signed in Stockholm on 22 May 2001, and Regulation (EU) 2019/1021 of the European Parliament
and of the Council(18).
(26) In accordance with the Stockholm Convention and Regulation (EU) 2019/1021, Member States are obliged to ensure
the protection of human health and the environment from persistent organic pollutants. Member States are required
to monitor the presence of persistent organic pollutants in the environment in accordance with Article 13(1), point
(d), of Regulation (EU) 2019/1021 implementing the requirements of Article 11(1) of the Stockholm Convention.
(27) Until now, river basin specific pollutants that are not identified as priority substances under Directive 2000/60/EC
have been subject to national EQS and been counted as physico-chemical quality elements supporting the
assessment of ecological status in surface waters. In groundwaters, it has also been possible for Member States to set
their own threshold values, even for man-made synthetic substances. That flexibility has led to sub-optimal results in
terms of comparability of the status of water bodies between Member States, and in terms of environmental
protection. Therefore, it is necessary to provide for a procedure that allows for an agreement at Union level on EQS
and threshold values that are to be applied for those substances if they are identified as being of national concern,
and to establish repositories of the applicable threshold values in Annex II to Directive 2006/118/EC and of the
applicable EQS in a new annex to Directive 2008/105/EC. The harmonised EQS and threshold values should only be
applied by Member States in assessing the status of their water bodies in the river basin districts where a risk has
been identified from those substances.
(28) Furthermore, integrating river basin specific pollutants into the definition of chemical status of surface waters
ensures a more coordinated, coherent and transparent approach in terms of monitoring and assessment of chemical
status of surface water bodies and of related information to the public. It also facilitates a more targeted approach to
identifying and implementing measures to address all ‘chemical related’ issues in a more holistic, effective and
efficient way. Therefore, the definitions of ‘ecological status’ and ‘chemical status’ should be modified and the scope
of ‘chemical status’ should be widened to cover also the river basin specific pollutants, hitherto part of the definition
of ‘ecological status’ in Annex V to Directive 2000/60/EC. As a result, the concept of EQS for river basin specific
pollutants and related procedures should be included in Directive 2008/105/EC. The status of a water body should
not be considered as having deteriorated merely because of that change.
(29) The surface water and groundwater watch list mechanisms aim to gather information on the presence and
distribution of substances of potential concern in the aquatic environment, which, to date, have been poorly
documented and for which there are often no standardised analytical methods available. In addition, for substances
listed in Annex I to Directive 2006/118/EC and in Annex I to Directive 2008/105/EC, the analytical methods
available on the market are not always sensitive enough to achieve the proposed quality standards. Developing new
methods and monitoring an increased number of substances, groups of substances, or indicators is challenging and
generates increased costs but also a need for strengthened administrative capacity in the Member States, especially
those with fewer resources. Therefore, the establishment of a joint monitoring facility for managing the monitoring
requirements, when so requested by the Member States, could help them in carrying out that challenging task, easing
their financial and administrative burdens. The Commission should assess the options for the establishment,
financing and functioning of such a monitoring facility. The use of such a facility should be voluntary, accessible to
all interested Member States and without prejudice to arrangements already in place at national level.
(17) OJ L 209, 31.7.2006, p. 3, ELI: http://data.europa.eu/eli/convention/2006/507/oj.
(18) Regulation (EU) 2019/1021 of the European Parliament and of the Council of 20 June 2019 on persistent organic pollutants (OJ
L 169, 25.6.2019, p. 45, ELI: http://data.europa.eu/eli/reg/2019/1021/oj).
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(30) Several judgments of the Court of Justice of the European Union have clarified the concept of deterioration of status.
A definition of deterioration of status should therefore be introduced into Directive 2000/60/EC. As referred to in
Annex V to that Directive, the status of a surface water body comprises both its ecological and chemical status and
the status of a groundwater body comprises both its quantitative and chemical status. Instead of referring to each of
those elements separately in the definition, reference should be made simply to Annex V to that Directive. If the
status of a quality element for surface water assessed as ‘bad’ or ‘failing to achieve good’ or the status of a quality
element for groundwater assessed as ‘poor’ deteriorates further, that deterioration should also be considered as
a deterioration of the status of the water body.
(31) The judgments of the Court of Justice of the European Union, combined with additions to the lists of substances as
well as stricter standards for existing pollutants, have rendered the application of the non-deterioration principle of
Directive 2000/60/EC more challenging, in particular for projects that have a negative short-term impact on water
bodies or projects and activities that have a negative impact on water bodies due to relocation of water or sediments
containing pollutants. In the case of projects causing a negative short-term impact on one or more quality elements
of a water body, it is essential to confirm that the negative impact on those quality elements is no longer detectable
after one year or, for biological quality elements, after a maximum of three years. To ascertain that the negative
impact is no longer present, it should be possible for Member States to use existing monitoring arrangements.
However, such arrangements might not be sufficient, for instance where status is usually determined by
extrapolation, or if the affected quality elements are different from those considered most sensitive to routine
pressures and impacts, and thus not regularly monitored. In those cases, the ex-post verification should be done
through supplementary and tailored monitoring. In the case of projects or activities having a negative impact on
water bodies due to relocation of polluted water or sediments, the pollutant concentrations in the source-water body
might decrease and those in the receiving water body might increase despite there being no overall change in
pollutant mass balance. Such activities include the discharge of contaminated drainage water from construction
works or the relocation of dredged sediments for flood protection or navigation and should be allowed, provided
that several criteria are met. Those criteria should include a requirement that all practicable steps, including
treatment, be taken to mitigate any adverse impact and that the receiving surface water body is already in
less-than-good chemical status with respect to most of the substances relocated, and in particular with respect to the
most persistent and bioaccumulative substances, such as PFAS, and that information relating to the criteria, and
reasons for the relocation, are provided in the relevant river basin management plan. The criteria are intended to
ensure that the overall level of protection of human health and the environment provided by Directive 2000/60/EC
is maintained. The relocation of polluted water or sediment should not detract from the quality of drinking water
resources, and a zone should therefore be established adjacent to any drinking water abstraction point where stricter
precautions are needed. If Member States have already established safeguard zones under Article 7 of Directive
2000/60/EC, or Article 8 of Directive (EU) 2020/2184, those zones might serve the purpose.
(32) The green transition and other activities of public interest, such as in the areas of security and defence, require
significant investments in and development of new technologies, which can be challenging to reconcile with the
objectives of Directive 2000/60/EC, for example if they require the mining and use of critical raw materials which
result in emissions of substances of emerging concern. It is important to assess potential risks to the environment or
human health from those substances. This should be taken into account when listing substances on the watch lists. It
is equally important to identify the potential conflicts between those overall objectives and develop appropriate
responses to them. This could be done as part of the implementation report drawn up by the Commission in
accordance with Article 18 of Directive 2000/60/EC.
(33) In order to ensure a harmonised approach and level playing field in the Union, the power to adopt acts in
accordance with Article 290 TFEU should be delegated to the Commission to amend Parts A and C of Annex II and
Annexes III and IV to Directive 2006/118/EC concerning guidelines for the establishment of threshold values by
Member States, information to be provided by Member States with regard to the pollutants and indicators of
pollution for which threshold values have been established, the assessment of groundwater chemical status and the
identification and reversal of significant and sustained upward trends.
(34) Given the need to swiftly adapt to scientific and technical knowledge and to ensure a harmonised approach and level
playing field in the Union in respect of the procedure on how to derive EQS for river basin specific pollutants, the
power to adopt acts in accordance with Article 290 TFEU should be delegated to the Commission to amend Part B of
Annex II to Directive 2008/105/EC.
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(35) The review of the list of priority substances in Part A of Annex I to Directive 2008/105/EC has concluded that
several priority substances are no longer of Union-wide concern and should therefore no longer be included in that
Annex. Those substances should therefore be considered as river basin specific pollutants and included in a new
annex to Directive 2008/105/EC together with their corresponding EQS.
(36) In order to ensure a level playing field in the Union and allow comparability of water body status between Member
States, there is a need to harmonise national threshold values for some man-made synthetic groundwater pollutants.
Threshold values should be established as necessary at Union level for pollutants which have an anthropogenic
origin or for the products of their degradation or decomposition, provided that those pollutants and degradation
products either do not occur naturally in groundwater, or, if identical natural counterparts exist, provided that their
natural background levels are, at most, low. Those threshold values should be included in the repository of
harmonised threshold values for man-made synthetic substances in groundwater of national, regional or local
concern in a new Part D of Annex II to Directive 2006/118/EC. A harmonised threshold value for individual
pharmaceuticals should be included for application by Member States to any pharmaceutical active substance
identified as posing a risk at national level unless a stricter standard or threshold value has been set specifically for
that substance at Union or national level.
(37) All provisions of Directive 2006/118/EC relating to the assessment of groundwater chemical status should be
adapted to the introduction of the third category of harmonised threshold values in a new Part D of Annex II to that
Directive, in addition to the quality standards set out in Annex I to that Directive and the national threshold values
set out in accordance with the methodology set out in Part A of Annex II to that Directive.
(38) To ensure effective and coherent decision-making and develop synergies with the work carried out in the framework
of other Union legislation on chemicals, ECHA should be given a permanent and clearly circumscribed role in the
prioritisation of substances to be included in the watch lists and in the lists of substances in Annexes I and II to
Directive 2008/105/EC and Annexes I and II to Directive 2006/118/EC, and in the derivation of appropriate
science-based quality standards. The Committee for Risk Assessment (RAC) and the Committee for Socio-Economic
Analysis (SEAC) of ECHA should facilitate the carrying out of certain tasks conferred on ECHA by providing
opinions. ECHA should also ensure better coordination between various pieces of environmental law through
increased transparency as regards pollutants on a watch list or the development of Union-wide or national EQS or
threshold values, by making relevant scientific reports publicly available. When deriving threshold values for
pharmaceutical substances, ECHA should liaise with the European Medicines Agency (EMA).
(39) The Fitness Check concluded that more frequent and streamlined electronic reporting is needed to foster better
implementation and enforcement of Union water legislation. In view of its role also to more regularly monitor the
state of pollution as described in the Zero Pollution Action Plan, the European Environment Agency (EEA) should
facilitate such more frequent and streamlined reporting of monitoring data by Member States. It is important that
this essential environmental information be made available to the public and to the Commission in a timely manner.
Without prejudice to the monitoring frequency obligations in Directives 2000/60/EC, 2006/118/EC and
2008/105/EC, and insofar as the monitoring obligations under those Directives have led to the generation of
new monitoring data, Member States should make the following data available to the public and to the EEA: (i) every
three years, monitoring data on biological quality elements in surface waters collected and validated during the
preceding three years; and (ii) every two years, monitoring data on chemical quality elements in surface water and
groundwater collected and validated during the preceding two years. This should take place through the existing
electronic data delivery mechanisms, such as the EEA’s Reportnet system, with data submission facilitated by
automation, aligned with the relevant Water Information System for Europe State of the Environment data flows.
Member States are encouraged to make available to the public and to the EEA the monitoring data on chemical
quality elements annually. The reporting of status will continue to take place in the six-yearly river basin
management plans. The administrative burden is expected to be limited insofar as Member States are already
required to make spatial data themes publicly available under Directive 2007/2/EC of the European Parliament and
of the Council(19) as well as under Directive (EU) 2019/1024 of the European Parliament and of the Council(20).
(19) Directive 2007/2/EC of the European Parliament and of the Council of 14 March 2007 establishing an Infrastructure for Spatial
Information in the European Community (INSPIRE) (OJ L 108, 25.4.2007, p. 1, ELI: http://data.europa.eu/eli/dir/2007/2/oj).
(20) Directive (EU) 2019/1024 of the European Parliament and of the Council of 20 June 2019 on open data and the re-use of public
sector information (OJ L 172, 26.6.2019, p. 56, ELI: http://data.europa.eu/eli/dir/2019/1024/oj).
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(40) The status assessment under Directive 2000/60/EC is based on the one-out-all-out-principle and it should remain so.
It is therefore important that Member States take all possible measures to achieve good status or potential, as
appropriate, in relation to each relevant individual quality element. At the same time, to ensure that progress or lack
thereof on individual quality elements is visible, even when not all of them reach good status or potential, and that
progress or lack thereof across the Member States can be compared, indicators of progress should be developed and
harmonised at Union level for the uniform presentation and reporting by Member States of the status or potential of
those individual quality elements in a disaggregated way. Those indicators of progress should be interpreted without
prejudice to the conclusions drawn from applying the one-out-all-out principle.
(41) Better integration of data flows reported to the EEA under Union water legislation and, in particular, of the
inventories of emissions required by Directive 2008/105/EC, with the data flows reported to the Industrial
Emissions Portal under Directive 2010/75/EU and Regulation (EU) 2024/1244 of the European Parliament and of
the Council(21), will make the inventory reporting in accordance with Article 5 of Directive 2008/105/EC simpler
and more efficient. At the same time, it will reduce administrative burden and peak workload in the preparation of
the river basin management plans. In combination with the abolition of interim reporting on progress on the
implementation of programmes of measures, which did not prove effective, this simplified reporting will allow
Member States to put more effort into reporting emissions which until recently were not covered by the legislation
on industrial emissions although they were covered by the emissions reporting under Article 5 of Directive
2008/105/EC.
(42) The Treaty of Lisbon amending the Treaty on European Union and the Treaty establishing the European
Community(22), signed at Lisbon on 13 December 2007, introduced a distinction between powers delegated to the
Commission to adopt delegated acts, that is non-legislative acts of general application to supplement or amend
certain non-essential elements of a legislative act, and the powers conferred upon the Commission to adopt
implementing acts, that is acts to ensure uniform conditions for implementing legally binding Union acts. Directives
2000/60/EC and 2006/118/EC should be aligned to the legal framework introduced by that Treaty.
(43) The empowerment in Article 20(1), first subparagraph, of Directive 2000/60/EC, which provides for the use of the
regulatory procedure with scrutiny, fulfils the criteria in Article 290(1) TFEU, since it concerns adaptations of the
Annexes to that Directive and adoption of rules supplementing it. It should therefore be converted to an
empowerment for the Commission to adopt delegated acts. The empowerment in Section 1.4.1(ix) of Annex V to
Directive 2000/60/EC, which provides for the use of the regulatory procedure with scrutiny, fulfils the criteria in
Article 291(2) TFEU since it concerns uniform conditions for implementing that Directive. It should therefore be
converted to an empowerment for the Commission to adopt implementing acts.
(44) The empowerment in Article 8(1) of Directive 2006/118/EC, which provides for the use of the regulatory procedure
with scrutiny, fulfils the criteria in Article 290(1) TFEU, since it concerns adaptations of Parts A and C of Annex II
and Annexes III and IV to that Directive. It should therefore be converted to an empowerment for the Commission
to adopt delegated acts.
(45) It is of particular importance that the Commission carry out appropriate consultations during its preparatory work
on delegated acts, including at expert level, and that those consultations be conducted in accordance with the
principles laid down in the Interinstitutional Agreement of 13 April 2016 on Better Law-Making(23). 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 the Member States’ experts, and their experts systematically have access to meetings
of Commission expert groups dealing with the preparation of delegated acts.
(21) Regulation (EU) 2024/1244 of the European Parliament and of the Council of 24 April 2024 on reporting of environmental data
from industrial , establishing an Industrial Emissions Portal and repealing Regulation (EC) No 166/2006 (OJ L, 2024/1244,
2.5.2024, ELI: http://data.europa.eu/eli/reg/2024/1244/oj).
(22) OJ C 306, 17.12.2007, p. 1, ELI: http://data.europa.eu/eli/treaty/lis/sign.
(23) OJ L 123, 12.5.2016, p. 1, ELI: http://data.europa.eu/eli/agree_interinstit/2016/512/oj.
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(46) The empowerment in Article 8(3) of Directive 2000/60/EC, which provides for the use of the regulatory procedure
with scrutiny, fulfils the criteria in Article 291(2) TFEU, since it concerns the adoption of technical specifications and
standardised methods for analysis and monitoring of water status and therefore aims at ensuring uniform conditions
for the harmonised implementation of that Directive. It should therefore be converted to an empowerment for the
Commission to adopt implementing acts. In order to ensure comparability of data, the empowerment should also be
extended to include the establishment of formats for reporting monitoring and status data in accordance with
Article 8(4) of Directive 2000/60/EC. The implementing powers conferred on the Commission should be exercised
in accordance with Regulation (EU) No 182/2011 of the European Parliament and of the Council(24).
(47) Member States’ experts should continue to be involved in the regular cooperation facilitated by the Common
Implementation Strategy for Directive 2000/60/EC and in particular in the working groups established under it, and
thus closely involved especially in the revision of the watch lists, the updates of the lists of pollutants and the
establishment of the reporting formats.
(48) In order to ensure uniform conditions for the implementation of Directive 2000/60/EC, implementing powers
should be conferred on the Commission to set out technical specifications and standardised methods for analysis and
monitoring of water status in accordance with Annex V to that Directive, to establish formats for the reporting of
monitoring and status data, to adopt the results of the intercalibration exercise and the values established for the
Member State monitoring system classifications in accordance with Section 1.4.1(ix) of Annex V to that Directive
and to adopt indicators of progress allowing comparison of the progress made by Member States towards achieving
the good status or potential of their water bodies. Those powers should be exercised in accordance with Regulation
(EU) No 182/2011.
(49) In order to ensure uniform conditions for the implementation of Directive 2006/118/EC, implementing powers
should be conferred on the Commission to adopt a groundwater watch list and to establish a list of relevant and
non-relevant metabolites of pesticide substances. Those powers should be exercised in accordance with Regulation
(EU) No 182/2011.
(50) In order to ensure uniform conditions for the implementation of Directive 2008/105/EC, implementing powers
should be conferred on the Commission to adopt standardised formats for the reporting of point-source emissions
not covered by Regulation (EU) 2024/1244 and of diffuse emissions to the EEA. Those powers should be exercised
in accordance with Regulation (EU) No 182/2011.
(51) It is necessary to take into account scientific and technical progress in the area of monitoring of the status of water
bodies in accordance with the monitoring requirements set out in Annex V to Directive 2000/60/EC. Therefore,
Member States should be allowed to use data and services from remote sensing technologies, earth observation, such
as Copernicus services, in situ sensors and devices, online water-quality monitoring systems, or citizen science data,
leveraging the opportunities offered by artificial intelligence, advanced data analysis and processing. In accordance
with the EU Digital Strategy, including its objectives for increased digitalisation of public services and businesses,
Member States are encouraged to tap the potential of digitalisation for water management and in particular for water
quality monitoring. It is important to assess the technical and economic feasibility of using online systems for the
continuous, precise and real-time monitoring of water quality, and develop, if appropriate, guidance on their
application. This could be done in the context of the Common Implementation Strategy for Directive 2000/60/EC,
with the aim of assisting Member States to digitalise, where possible and appropriate, their water quality monitoring
techniques. Member States that have taken measures to digitalise monitoring techniques are encouraged to include
a summary of those measures in their river basin management plans.
(52) Member States should encourage deployment of digital tools such as remote sensing technologies and earth
observation, such as Copernicus services.
(53) The competent authorities should support training, skills development programmes and investment in human
capital to support the effective implementation of the best technologies and innovative solutions within the
framework of Directive 2000/60/EC.
(24) Regulation (EU) No 182/2011 of the European Parliament and of the Council of 16 February 2011 laying down the rules and
general principles concerning mechanisms for control by Member States of the Commission’s exercise of implementing powers (OJ
L 55, 28.2.2011, p. 13, ELI: http://data.europa.eu/eli/reg/2011/182/oj).
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(54) In accordance with the Convention on Access to Information, Public Participation in Decision-Making and Access to
Justice in Environmental Matters(25), signed in Aarhus on 25 June 1998, members of the public concerned are to
have access to justice in order to contribute to the protection of the right to live in an environment which is
adequate for personal health and well-being. Therefore Member States should ensure access to justice under Directive
2000/60/EC in accordance with that Convention. Moreover, according to settled case law of the Court of Justice of
the European Union, it is for the courts of the Member States to ensure judicial protection of a person’s rights under
Union law. Furthermore, Article 19(1) of the Treaty on European Union (TEU) requires Member States to provide
remedies sufficient to ensure effective judicial protection in the fields covered by Union law.
(55) Considering the increases in unforeseeable weather events, in particular extreme floods and prolonged droughts, and
in significant pollution incidents resulting in or exacerbating transboundary accidental pollution, Member States
should be required to ensure that information on such incidents is provided without delay to other potentially
affected Member States and effectively cooperate with such Member States to mitigate the effects of the event or
incident. It is also necessary to reinforce cooperation between Member States and streamline procedures for
transboundary cooperation in the case of more structural, i.e. non-accidental and longer-term transboundary issues
which cannot be solved at Member State level, in accordance with Article 12 of Directive 2000/60/EC. Where
Member States have already established effective cooperation, this should be taken into account. If Union assistance
is necessary, competent national authorities can send requests for assistance to the Emergency Response
Coordination Centre of the Commission, which will facilitate the coordination of the provision of the required
assistance through the Union Civil Protection Mechanism, in accordance with Article 15 of Decision
No 1313/2013/EU of the European Parliament and of the Council(26). Moreover, considering that river basin
districts can also extend beyond the territory of the Union, it is important to ensure that Member States effectively
implement Directive 2000/60/EC within their respective territories. Member States should also endeavour to
establish appropriate coordination with the relevant third countries which would contribute to the fulfilment of the
objectives set out in that Directive for those specific river basin districts.
(56) The Commission should report on the possibility of including an extended producer responsibility mechanism in
Directive 2000/60/EC. That report should take into account experience gained in particular from implementing the
provisions concerning extended producer responsibility in the Union legislation on urban waste-water treatment,
waste, and single-use plastics.
(57) Directives 2000/60/EC, 2006/118/EC and 2008/105/EC should therefore be amended accordingly.
(58) Since the objectives of this Directive, namely to ensure a high level of environmental protection and an improvement
of the environmental quality of European freshwaters, cannot be sufficiently achieved by Member States alone but
can rather, by reason of the transboundary nature of water pollution, be better achieved at Union level, the Union
may adopt measures in accordance with the principle of subsidiarity as set out in Article 5 TEU. 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,
HAVE ADOPTED THIS DIRECTIVE:
Article 1
Amendments to Directive 2000/60/EC
Directive 2000/60/EC is amended as follows:
(1) in Article 1(e), the fourth indent is replaced by the following:
‘— achieving the objectives of relevant international agreements, including those which aim to prevent and eliminate
pollution of the marine environment, by Union action to cease or phase out discharges, emissions and losses of
priority hazardous substances, with the ultimate aim of achieving concentrations in the marine environment near
background values for naturally occurring substances and close to zero for man-made synthetic substances.’;
(25) OJ L 124, 17.5.2005, p. 4, ELI: http://data.europa.eu/eli/convention/2005/370/oj.
(26) Decision No 1313/2013/EU of the European Parliament and of the Council of 17 December 2013 on a Union Civil Protection
Mechanism (OJ L 347, 20.12.2013, p. 924, ELI: http://data.europa.eu/eli/dec/2013/1313/oj).
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(2) Article 2 is amended as follows:
(a) point 24 is replaced by the following:
‘24. “Good surface water chemical status” means the chemical status required to meet the environmental
objectives for surface waters set out in Article 4(1)(a) of this Directive, that is the chemical status achieved by
a body of surface water in which concentrations of pollutants exceed neither the environmental quality
standards for priority substances listed in Part A of Annex I to Directive 2008/105/EC of the European
Parliament and of the Council(*) nor the environmental quality standards for river basin specific pollutants
set and applied in accordance with Article 8d of that Directive, and in which effect-based trigger values, where
available, are also not exceeded.
(*) Directive 2008/105/EC of the European Parliament and of the Council of 16 December 2008 on
environmental quality standards in the field of water policy, amending and subsequently repealing Council
Directives 82/176/EEC, 83/513/EEC, 84/156/EEC, 84/491/EEC, 86/280/EEC and amending Directive
2000/60/EC of the European Parliament and of the Council (OJ L 348, 24.12.2008, p. 84, ELI: http://data.
europa.eu/eli/dir/2008/105/oj).’;
(b) point 30 is replaced by the following:
‘30. “Priority substances” means substances listed in Part A of Annex I to Directive 2008/105/EC, that are
substances which present a significant risk to or via the aquatic environment and are prioritised in accordance
with Article 16(2) of this Directive.’;
(c) the following points are inserted:
‘30a. “Priority hazardous substances” means priority substances which are identified as “hazardous” in accordance
with the legislation referred to in Article 16(3).
30b. “River basin specific pollutants” means pollutants that are not or no longer identified as priority substances,
but which Member States have identified, on the basis of the assessment of pressures and impacts on surface
water bodies carried out in accordance with Annex II, as being discharged or deposited in significant
quantities into a river basin or sub-basin and thus posing a significant risk to or via the aquatic environment
within their territory.’;
(d) point 35 is replaced by the following:
‘35. “Environmental quality standard” means the concentration of a particular pollutant or group of pollutants in
water, sediment or biota not to be exceeded in order to protect human health and the environment.’;
(e) the following point is inserted:
‘35a. “Effect-based trigger value” means a threshold for the effects of a pollutant or group of pollutants in water,
sediment or biota, where those effects are measured by an appropriate and scientifically validated
effect-based monitoring method, above which adverse effects on human health or the environment from
that pollutant or group of pollutants in water, sediment or biota, could occur.’;
(f) point 37 is replaced by the following:
‘37. “Water intended for human consumption” means water intended for human consumption as defined in
Article 2, point (1), of Directive (EU) 2020/2184 of the European Parliament and of the Council(*).
(*) Directive (EU) 2020/2184 of the European Parliament and of the Council of 16 December 2020 on the
quality of water intended for human consumption (OJ L 435, 23.12.2020, p. 1, ELI: http://data.europa.eu/eli/
dir/2020/2184/oj).’;
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(g) the following point is added:
‘42. “Deterioration of the status of a body of water” means the lowering of the status of at least one of the quality
elements, within the meaning of Annex V, by one class, even if that lowering does not result in a fall in the
classification of the body of water as a whole; however, if a quality element is already at the lowest class, any
further deterioration of that element constitutes a deterioration of the status of the body of water.’;
(3) Article 4 is amended as follows:
(a) paragraph 1 is amended as follows:
(i) in point (a), points (i), (ii) and (iii) are replaced by the following:
‘(i) Member States shall implement the necessary measures to prevent deterioration of the status of all bodies
of surface water, subject to the application of paragraphs 6 to 7b and without prejudice to paragraph 8;
(ii) Member States shall protect, enhance and restore all bodies of surface water, subject to the application of
point (iii) of this paragraph for artificial and heavily modified bodies of water, with the aim of achieving
good surface water status at the latest 15 years after the date of entry into force of this Directive, in
accordance with the provisions laid down in Annex V, subject to the application of extensions determined
in accordance with paragraph 4 and to the application of paragraphs 5 to 7b without prejudice to
paragraph 8;
(iii) Member States shall protect and enhance all artificial and heavily modified bodies of water, with the aim
of achieving good ecological potential and good surface water chemical status at the latest 15 years from
the date of entry into force of this Directive, in accordance with the provisions laid down in Annex V,
subject to the application of extensions determined in accordance with paragraph 4 and to the application
of paragraphs 5 to 7b without prejudice to paragraph 8;’;
(ii) in point (b), points (i) and (ii), are replaced by the following:
‘(i) Member States shall implement the measures necessary to prevent or limit the input of pollutants into
groundwater and to prevent the deterioration of the status of all bodies of groundwater, subject to the
application of paragraphs 6 to 7b of this Article and without prejudice to paragraph 8 thereof and subject
to the application of Article 11(3)(j);
(ii) Member States shall protect, enhance and restore all bodies of groundwater and ensure a balance between
abstraction and recharge of groundwater, with the aim of achieving good groundwater status at the latest
15 years after the date of entry into force of this Directive, in accordance with the provisions laid down in
Annex V, subject to the application of extensions determined in accordance with paragraph 4 of this
Article and to the application of paragraphs 5 to 7b thereof without prejudice to paragraph 8 of this
Article and subject to the application of Article 11(3)(j);’;
(iii) in point (b)(iii), the second subparagraph is replaced by the following:
‘Measures to achieve trend reversal shall be implemented in accordance with Article 17(2) of this Directive and
Article 5 and Annex IV of Directive 2006/118/EC of the European Parliament and of the Council(*), subject to
the application of paragraphs 6 to 7b of this Article and without prejudice to paragraph 8 thereof.
(*) Directive 2006/118/EC of the European Parliament and of the Council of 12 December 2006 on the
prevention and control of groundwater pollution (OJ L 372, 27.12.2006, p. 19, ELI: http://data.europa.
eu/eli/dir/2006/118/oj)’;
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(b) the following paragraphs are inserted:
‘7a. Member States will not be in breach of this Directive when any negative short-term impact on one or more
quality elements of a body of water caused by a new project or a modification to an existing project in that body of
water is no longer detectable after one year or, for biological quality elements, after a maximum of three years
beyond initiation of the execution of the project, and all the following conditions are met:
(a) the negative impact is not the result of direct discharges, emissions or losses of a pollutant;
(b) the potential for the negative impact to occur is reliably assessed ex ante by a competent authority, and it is
concluded that there would be no negative impact for the body of water concerned or any connected body of
water after one year or, for biological quality elements, after a maximum of three years;
(c) an ex post verification is carried out;
(d) all practicable measures are taken to mitigate any negative impacts on the body and any connected bodies of
water; and
(e) a summary of the main activities carried out in accordance with this paragraph, the relevant ex post verification
results, and the measures taken to mitigate negative impacts, is included in the river basin management plan
required under Article 13.
For the purposes of carrying out the ex -post verification under point (c) of the first subparagraph, existing
monitoring arrangements set up pursuant to Annex V may be used and, where necessary, they shall be
supplemented by additional ad-hoc monitoring.
7b. Member States will not be in breach of this Directive when deterioration occurs in the status of a receiving
body of surface water as a result of relocating, by human activity, water or sediment from the same or another
body of surface water, or from a body of groundwater to the receiving body of surface water, without causing a net
increase in pollutant load, and all the following conditions are met:
(a) all practicable steps, in particular the treatment of the water or sediment, if feasible, to minimise the transfer of
pollutant load are taken to mitigate the adverse impact on the status of the bodies of water impacted by the
relocation;
(b) the composition of the water or sediments to be relocated is established, and the relocation does not increase
the overall risk to human health and the environment compared to the existing risk prior to the relocation;
(c) the receiving body of surface water is confirmed as already not being in good chemical status with respect to
most of the pollutants relocated, and in particular with respect to the most persistent and bioaccumulative
pollutants relocated, and the ecological status or potential of the receiving body of water is not expected to fall
into a lower class as a result of the relocation of those pollutants;
(d) the relocation shall not result in an increase in the purification treatment required for the production of
drinking water;
(e) within the receiving body of water, a zone where relocation is prohibited has been established around any
abstraction point for water intended for human consumption;
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(f) there are no significantly better environmental options for reasons of technical feasibility or disproportionate
cost;
(g) the relocation is subject to prior regulation or authorisation; and
(h) a summary, including information related to points (a) to (g) of this paragraph and the reasons for the
relocation, is included in the river basin management plan required under Article 13.’;
(c) paragraphs 8 and 9 are replaced by the following:
‘8. When applying paragraphs 3 to 7b, Member States shall ensure that the achievement of the objectives of
this Directive in other bodies of water within the same river basin district is not thereby permanently excluded or
compromised and that the application of those provisions is consistent with the implementation of other Union
environmental legislation.
9. Member States shall take steps to ensure that the application of the new provisions, including the application
of paragraphs 3 to 7b, guarantees at least the same level of protection as the existing Union legislation.’;
(4) Article 7(2) is replaced by the following:
‘2. For each body of water identified under paragraph 1 of this Article, in addition to meeting the objectives of
Article 4 of this Directive in accordance with the requirements of this Directive, and for surface water bodies including
the quality standards established at Union level in accordance with Article 16 of this Directive, Member States shall
ensure that under the water treatment regime applied, and in accordance with Union legislation, the resulting water
will meet the requirements of Directive (EU) 2020/2184.’;
(5) Article 8 is amended as follows:
(a) paragraph 3 is replaced by the following:
‘3. The Commission is empowered to adopt implementing acts to set out technical specifications and
standardised methods for analysis and monitoring of water status in accordance with Annex V, to establish formats
for the reporting of monitoring and status data, to adopt the results of the intercalibration exercise and the values
established for the Member State monitoring system classifications in accordance with Section 1.4.1(ix) of
Annex V, and to adopt indicators of progress allowing comparison of the progress made by Member States
towards achieving the good status or potential of their water bodies. When establishing the formats for the
reporting of monitoring and status data, the Commission may avail itself of technical and scientific support
available from the European Environment Agency (EEA). Those implementing acts shall be adopted in accordance
with the examination procedure referred to in Article 21(2).’;
(b) the following paragraphs are added:
‘4. Member States shall ensure that the available and validated monitoring data on biological quality elements in
surface waters collected in accordance with Section 1.3 of Annex V to this Directive are made available to the
public and to the EEA every three years, and that the available and validated monitoring data on chemical quality
elements in surface waters and groundwater collected in accordance with Sections 1.3 and 2.4 of Annex V to this
Directive are made available to the public and to the EEA every two years electronically in accordance with
Directives 2003/4/EC(1)*, 2007/2/EC(2)*and (EU) 2019/1024(3)*of the European Parliament and of the Council.
For those purposes, Member States shall use the formats established in accordance with paragraph 3 of this Article
and automated reporting and data delivery mechanisms aligned with the relevant Water Information System for
Europe State of the Environment data flows.
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5. The EEA shall ensure that the information made available in accordance with paragraph 4 is regularly
processed and analysed for the purpose of making it available, via relevant Union portals, for reuse by the
Commission and relevant Union agencies and for the purpose of providing the Commission, the Member States
and the public with objective, reliable and comparable information, in accordance with Regulation (EC)
No 401/2009 of the European Parliament and of the Council(4)*.
6. By 11 November 2027, the Commission shall publish a report on options for the establishment, financing
and functioning of a European Union joint monitoring facility.
The report shall take into account, inter alia, the following:
(a) the voluntary nature of the use of such a joint monitoring facility;
(b) the scope of the analyses to be performed by such a facility, including the range of substances and indicators to
be covered from the lists established under this Directive, Directive 2006/118/EC and Directive 2008/105/EC
of the European Parliament and of the Council(5)*;
(c) the sources of funding for such a facility, which may include Union co-funding;
(d) the operating model of such a facility, considering both centralised and decentralised options;
Following the report, the Commission shall, where appropriate, present a legislative proposal in order to establish
a European Union joint monitoring facility.
(1)* Directive 2003/4/EC of the European Parliament and of the Council of 28 January 2003 on public access to
environmental information and repealing Council Directive 90/313/EEC (OJ L 41, 14.2.2003, p. 26,
ELI: http://data.europa.eu/eli/dir/2003/4/oj).
(2)* Directive 2007/2/EC of the European Parliament and of the Council of 14 March 2007 establishing an
Infrastructure for Spatial Information in the European Community (INSPIRE) (OJ L 108, 25.4.2007, p. 1,
ELI: http://data.europa.eu/eli/dir/2007/2/oj).
(3)* Directive (EU) 2019/1024 of the European Parliament and of the Council of 20 June 2019 on open data and
the re-use of public sector information (OJ L 172, 26.6.2019, p. 56, ELI: http://data.europa.eu/eli/dir/2019/
1024/oj).
(4)* Regulation (EC) No 401/2009 of the European Parliament and of the Council of 23 April 2009 on the
European Environment Agency and the European Environment Information and Observation Network (OJ
L 126, 21.5.2009, p. 13, ELI: http://data.europa.eu/eli/reg/2009/401/oj).
(5)* Directive 2008/105/EC of the European Parliament and of the Council of 16 December 2008 on
environmental quality standards in the field of water policy, amending and subsequently repealing Council
Directives 82/176/EEC, 83/513/EEC, 84/156/EEC, 84/491/EEC, 86/280/EEC and amending Directive
2000/60/EC of the European Parliament and of the Council (OJ L 348, 24.12.2008, p. 84, ELI: http://data.
europa.eu/eli/dir/2008/105/oj).’;
(6) Article 10 is amended as follows:
(a) paragraph 2 is replaced by the following:
‘2. For the purpose of complying with the objectives, quality standards and threshold values established
pursuant to this Directive, Member States shall ensure the establishment and implementation of the following:
(a) emission controls based on best available techniques;
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(b) relevant emission limit values;
(c) in the case of diffuse impacts, controls including, as appropriate, best environmental practices,
in accordance with Council Directive 91/676/EEC(*)and Directives 2009/128/EC(**), 2010/75/EU(***)and (EU)
2024/3019(****) of the European Parliament and of the Council, as well as any other Union legislation relevant
for addressing point source or diffuse pollution including any relevant legislation adopted in accordance with
Article 16 of this Directive.
(*) Council Directive 91/676/EEC of 12 December 1991 concerning the protection of waters against pollution
caused by nitrates from agricultural sources (OJ L 375, 31.12.1991, p. 1, ELI: http://data.europa.eu/eli/dir/
1991/676/oj).
(**) Directive 2009/128/EC of the European Parliament and of the Council of 21 October 2009 establishing
a framework for Community action to achieve the sustainable use of pesticides (OJ L 309, 24.11.2009,
p. 71, ELI: http://data.europa.eu/eli/dir/2009/128/oj).
(***) Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial
and livestock rearing emissions (integrated pollution prevention and control) (OJ L 334, 17.12.2010, p. 17,
ELI: http://data.europa.eu/eli/dir/2010/75/oj).
(****)Directive (EU) 2024/3019 of the European Parliament and of the Council of 27 November 2024 concerning
urban wastewater treatment (OJ L, 2024/3019, 12.12.2024, ELI: http://data.europa.eu/eli/dir/2024/3019/
oj).’;
(b) paragraph 3 is replaced by the following;
‘3. Where a quality objective, quality standard or threshold, whether established pursuant to this Directive, to
Directives 2006/118/EC or 2008/105/EC, or pursuant to any other Union legislation, requires stricter conditions
than those which would result from the application of paragraph 2, more stringent emission controls shall be set
accordingly.’;
(7) Article 11 is amended as follows:
(a) the following paragraph is inserted:
‘1a. In addressing chemical pollution, Member States shall, where possible, prioritise source-control measures
in accordance with the relevant Union sectoral legislation on pollution. Where necessary, measures to reduce the
risk from potential pollutants already in products and from pollutants already in the environment shall also be
considered for the purpose of achieving the good status of water bodies.’;
(b) in paragraph 3, point (k) is replaced by the following:
‘(k) in accordance with action taken pursuant to Article 16, measures to eliminate pollution of surface waters by
priority hazardous substances and to progressively reduce pollution by other substances which would
otherwise prevent Member States from achieving the environmental objectives for the bodies of surface waters
set out in Article 4;’;
(c) in paragraph 5, the second indent is replaced by the following:
‘— relevant permits and authorisations are reviewed and revised, as appropriate,’;
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(8) Article 12 is replaced by the following:
‘Article 12
Issues which cannot be dealt with at Member State level
1. Where a Member State identifies an issue which has an impact on the management of its water but which cannot
be resolved by that Member State, it shall notify the issue to the competent authorities of any relevant Member State
and, where an international river basin district is concerned, to any relevant coordination structure identified under
Article 3(4) and make recommendations for the resolution of it.
2. The Member States concerned shall cooperate to identify the sources of the issues referred to in paragraph 1 and
the measures required for addressing those issues.
Member States shall respond to each other in a timely manner and no later than three months after the notification
referred to paragraph 1.
3. The Commission shall be informed of, and be invited to assist in, any cooperation referred to in paragraph 2 of
this Article. Where appropriate, the Commission shall, taking into account the plans reported pursuant to Article 15,
consider whether further action needs to be taken at Union level in order to reduce the transboundary impacts on
water bodies.;
4. The Commission shall comment within a period of six months on any recommendations received from Member
States in the context of the cooperation referred to in paragraphs 2 and 3.
5. Where a Member State faces exceptional circumstances of natural or anthropogenic origin or force majeure, in
particular extreme floods and prolonged droughts, or significant pollution incidents, which could affect water bodies
situated in other Member States, it shall ensure that the competent authorities for the affected water bodies in those
Member States, as well as any relevant coordination structure identified under Article 3(4) for an international river
basin, and the Commission, are informed without delay, and that the necessary cooperation, if not already in place, is
established between the Member States affected and used to investigate the causes and address the consequences of the
exceptional circumstances or incidents and mobilise emergency response as appropriate.’;
(9) the following Article is inserted:
‘Article 14a
Access to justice
1. In line with the objective of contributing to the implementation of the Convention on Access to Information,
Public Participation in Decision-Making and Access to Justice in Environmental Matters(*), signed in Aarhus on
25 June 1998, Member States shall ensure that in accordance with the relevant national legal system, members of the
public concerned have access to a review procedure before a court of law or another independent and impartial body
established by law, to challenge the substantive or procedural legality of decisions, acts or omissions subject to
Articles 4 and 11 and Article 13(1) of this Directive, where at least one of the following conditions is met:
(a) they have a sufficient interest; or
(b) they maintain the impairment of a right, where administrative procedural law of a Member State requires this as
a precondition.
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2. Member States shall determine what constitutes a sufficient interest and impairment of a right, consistent with
the objective of giving the public concerned wide access to justice. To this end, the interest of any non-governmental
organisation promoting environmental protection and meeting any requirements under national law shall be deemed
sufficient for the purpose of paragraph 1(a). Such organisations shall also be deemed to have rights capable of being
impaired for the purpose of paragraph 1(b).
3. Standing in the review procedure shall not be conditional on the role that the member of the public concerned
played during a participatory phase of the decision-making procedures under this Directive.
4. Member States shall determine at what stage the decisions, acts or omissions referred to in paragraph 1 may be
challenged.
5. The review procedure shall be fair, equitable, timely and not prohibitively expensive, and shall provide for
adequate and effective redress mechanisms, including injunctive relief where appropriate.
6. Member States shall ensure that practical information is made available to the public on access to administrative
and judicial review procedures referred to in this Article.
(*) OJ L 124, 17.5.2005, p. 4, ELI: http://data.europa.eu/eli/convention/2005/370/oj.’;
(10) in Article 15, paragraph 3 is deleted;
(11) Article 16 is replaced by the following:
‘Article 16
Strategies against pollution of water
1. The European Parliament and the Council shall adopt specific measures against pollution of water by individual
pollutants or groups of pollutants presenting a significant risk to or via the aquatic environment, including such risks
to waters used for the abstraction of drinking water. For those pollutants, measures shall be aimed at the progressive
reduction of priority substances, as defined in Article 2(30), and at the cessation or phasing-out of discharges,
emissions and losses of priority hazardous substances, as defined in Article 2(30a). Such measures shall be adopted
acting on the proposals presented by the Commission in accordance with the procedures laid down in the Treaty.
2. The Commission shall review the list of priority substances and the corresponding EQS for those substances set
out in Part A of Annex I to Directive 2008/105/EC by 11 May 2032 and every six years thereafter, and, where
appropriate, accompany the review with a legislative proposal to update the list of priority substances and the
corresponding EQS in surface water, sediment or biota. In conducting the review, the Commission shall prioritise
substances for action on the basis of risk to or via the aquatic environment, identified by:
(a) risk assessment carried out under Directive 2001/83/EC of the European Parliament and of the Council(1)*,
Regulation (EC) No 1907/2006 of the European Parliament and of the Council(2)*, Directive 2009/128/EC and
Regulations (EC) No 1107/2009(3)*, (EU) No 528/2012(4)*and (EU) 2019/6(5)*of the European Parliament and
of the Council; or
(b) a simplified risk-based assessment procedure based on scientific principles, taking particular account of:
— evidence regarding the intrinsic hazard of the substance concerned, and in particular its aquatic ecotoxicity and
human toxicity via aquatic exposure routes,
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— evidence from monitoring of widespread environmental contamination, including monitoring data reported
by the Member States to the Commission in accordance with Article 8b(4) of Directive 2008/105/EC, and
— other proven factors which could indicate the possibility of widespread environmental contamination, such as
production or use volume of the substance concerned, and use patterns.
3. In the course of the review referred to in paragraph 2, the Commission shall categorise, where appropriate, the
priority substances into one or more of the following categories:
(a) priority hazardous substances;
(b) substances behaving like ubiquitous persistent bioaccumulative and toxic substances (uPBTs);
(c) substances that tend to accumulate in sediment or in biota, or in both.
In doing so, the Commission shall take into account the identification of substances of concern under other, relevant,
Union legislation concerning hazardous substances, including Regulation (EC) No 1272/2008 of the European
Parliament and of the Council(6)*, in relevant international agreements, and in relevant scientific reports. Particular
account shall be taken of substances meeting the criteria in Article 57 of Regulation (EC) No 1907/2006 where the
criteria of concern are relevant to the aquatic environment.
3a. As part of the review and accompanying proposal referred to in paragraph 2 of this Article the Commission
shall, where appropriate, propose the deselection of substances from the list of substances in Part A of Annex I to
Directive 2008/105/EC if they no longer pose a significant risk to or via the aquatic environment within the Union
and include them in the repository of harmonised EQS for river basin specific pollutants in Part C of Annex II to that
Directive. The proposal shall take into account the results of Member States’ assessments of pressures and impacts on
surface water bodies carried out in accordance with Annex II to this Directive. Member States shall implement the
corresponding harmonised EQS if the pollutants are of national or regional concern, in accordance with Article 8d of
Directive 2008/105/EC.
4. The Commission shall review the list of river basin specific pollutants and corresponding EQS in Part C of
Annex II to Directive 2008/105/EC by 11 May 2032 and every six years thereafter, and, where appropriate,
accompany the review with a legislative proposal to update that list.
4a. When identifying river basin specific pollutants for which it could be necessary to set EQS at Union level, the
Commission shall take into account the following criteria:
(a) the risk posed by the pollutants, including their hazard, their environmental concentrations and the concentration
above which effects might be expected, as well as possible cumulative effects;
(b) the disparity between the national EQS set for river basin specific pollutants by different Member States and the
degree to which such disparity is justifiable;
(c) the number of Member States already implementing EQS for the river basin specific pollutants under
consideration.
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4b. The Commission shall review the indicative list of categories of river basin specific pollutants set out in Part
A of Annex II to Directive 2008/105/EC by 11 May 2032 and every six years thereafter, and where appropriate,
accompany the review with a legislative proposal to update that list.
5. For the purpose of assisting the Commission in its review of Annexes I and II to Directive 2008/105/EC, the
European Chemicals Agency (ECHA) shall prepare scientific reports, which shall take account of the following:
(a) the opinions of the Committee for Risk Assessment (RAC) and the Committee for Socio-Economic Analysis
(SEAC) of ECHA;
(b) the results of the monitoring programmes established in accordance with Article 8 of this Directive;
(c) the monitoring data collected in accordance with Article 8b(4) of Directive 2008/105/EC;
(d) the outcome of the reviews of the Annexes to Directives 2006/118/EC and (EU) 2020/2184;
(e) requirements to address soil pollution, including related monitoring data;
(f) Union research programmes and scientific publications, including information resulting from remote sensing
technologies, earth observation, such as Copernicus services, in situ sensors and devices, and citizen science data,
leveraging the opportunities offered by artificial intelligence, advanced data analysis and processing;
(g) comments and information from relevant stakeholders; and
(h) recommendations from the working groups established under the Common Implementation Strategy for Directive
2000/60/EC.
By 11 May 2030 and every six years thereafter, ECHA shall prepare and make publicly available a report summarising
the findings of the scientific reports prepared under this paragraph.
6. The Commission shall submit proposals, where appropriate, for controls to achieve:
(a) the progressive reduction of discharges, emissions and losses of priority substances; and
(b) in particular the cessation or phasing-out of discharges, emissions and losses of the priority hazardous substances
as identified in accordance with paragraph 3, including, where appropriate, a timetable for doing so within 20
years of the designation of the substances as priority hazardous substances.
In doing so, the Commission shall identify the appropriate cost-effective and proportionate level and combination of
product and process controls for both point and diffuse sources and take account of Union-wide uniform emission
limit values for process controls. Where appropriate, action at Union level for process controls may be established on
a sector-by-sector basis. Where product or process controls include a review of the relevant authorisations or
substance approvals issued under Directive 2001/83/EC, Regulation (EC) No 1907/2006, Directive 2009/128/EC,
Regulation (EC) No 1107/2009, Directive 2010/75/EU, Regulation (EU) No 528/2012 or Regulation (EU) 2019/6,
such reviews shall be carried out in accordance with the provisions of those Directives and Regulations as indicated in
Article 7a of Directive 2008/105/EC. Such reviews shall take into account the Commission’s assessment in accordance
with Article 7a(1) of Directive 2008/105/EC. Each proposal for controls shall, where appropriate, specify
arrangements for their review and updating and for the assessment of their effectiveness.
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9. The Commission may prepare strategies against water pollution by any other pollutants or groups of pollutants,
including any such pollution which occurs as a result of accidents.
(1)* Directive 2001/83/EC of the European Parliament and of the Council of 6 November 2001 on the Community
code relating to medicinal products for human use (OJ L 311, 28.11.2001, p. 67, ELI: http://data.europa.eu/eli/
dir/2001/83/oj).
(2)* Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006
concerning the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH), establishing
a European Chemicals Agency, amending Directive 1999/45/EC and repealing Council Regulation (EEC)
No 793/93 and Commission Regulation (EC) No 1488/94 as well as Council Directive 76/769/EEC and
Commission Directives 91/155/EEC, 93/67/EEC, 93/105/EC and 2000/21/EC (OJ L 396, 30.12.2006, p. 1,
ELI: http://data.europa.eu/eli/reg/2006/1907/oj).
(3)* Regulation (EC) No 1107/2009 of the European Parliament and of the Council of 21 October 2009 concerning
the placing of plant protection products on the market and repealing Council Directives 79/117/EEC and
91/414/EEC (OJ L 309, 24.11.2009, p. 1, ELI: http://data.europa.eu/eli/reg/2009/1107/oj).
(4)* Regulation (EU) No 528/2012 of the European Parliament and of the Council of 22 May 2012 concerning the
making available on the market and use of biocidal products (OJ L 167, 27.6.2012, p. 1, ELI: http://data.europa.
eu/eli/reg/2012/528/oj).
(5)* Regulation (EU) 2019/6 of the European Parliament and of the Council of 11 December 2018 on veterinary
medicinal products and repealing Directive 2001/82/EC (OJ L 4, 7.1.2019, p. 43, ELI: http://data.europa.eu/eli/
reg/2019/6/oj).
(6)* Regulation (EC) No 1272/2008 of the European Parliament and of the Council of 16 December 2008 on
classification, labelling and packaging of substances and mixtures, amending and repealing Directives
67/548/EEC and 1999/45/EC, and amending Regulation (EC) No 1907/2006 (OJ L 353, 31.12.2008, p. 1,
ELI: http://data.europa.eu/eli/reg/2008/1272/oj).’;
(12) in Article 17, paragraphs 4 and 5 are deleted;
(13) in Article 18, paragraph 4 is deleted;
(14) the following Article is inserted:
‘Article 19a
Report on an extended producer responsibility mechanism
By 11 May 2029, the Commission shall publish a report on the possibility to include in this Directive an extended
producer responsibility mechanism. The report shall evaluate in particular the feasibility of requiring producers to
contribute to the costs of monitoring programmes designed under Article 8 of this Directive if those producers place
on the Union market products that contain any of the substances listed in Annex I to Directive 2006/118/EC or in
Annex I to Directive 2008/105/EC.’;
(15) Articles 20 and 21 are replaced by the following:
‘Article 20
Technical adaptations and implementation of this Directive
The Commission is empowered to adopt delegated acts in accordance with Article 20a to amend Annexes I and III and
Section 1.3.6 of Annex V in order to adapt the information requirements related to competent authorities, the content
of the economic analysis and the selected monitoring standards, respectively, to scientific and technical progress.
Article 20a
Exercise of the delegation
1. The power to adopt delegated acts is conferred on the Commission subject to the conditions laid down in this
Article.
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2. The power to adopt delegated acts referred to in Article 20 shall be conferred on the Commission for an
indeterminate period of time from 10 May 2026.
3. The delegation of power referred to in Article 20 may be revoked at any time by the European Parliament and by
the Council. A decision to revoke shall put an end to the delegation of the power specified in that decision. It shall take
effect the day following the publication of the decision in the Official Journal of the European Union or at a later date
specified therein. It shall not affect the validity of the delegated acts already in force.
4. Before adopting a delegated act, the Commission shall consult experts designated by each Member State in
accordance with the principles laid down in the Interinstitutional Agreement of 13 April 2016 on Better Law-Making.
5. As soon as it adopts a delegated act, the Commission shall notify it simultaneously to the European Parliament
and to the Council.
6. A delegated act adopted pursuant to Article 20 shall enter into force only if no objection has been expressed
either by the European Parliament or by the Council within a period of two months of notification of that act to the
European Parliament and the Council or if, before the expiry of that period, the European Parliament and the Council
have both informed the Commission that they will not object. That period shall be extended by two months at the
initiative of the European Parliament or of the Council.
Article 21
Committee procedure
1. The Commission shall be assisted by a committee. That committee shall be a committee within the meaning of
Regulation (EU) No 182/2011 of the European Parliament and of the Council(*).
2. Where reference is made to this paragraph, Article 5 of Regulation (EU) No 182/2011 shall apply.
Where the committee delivers no opinion, the Commission shall not adopt the draft implementing act and
Article 5(4), third subparagraph, of Regulation (EU) No 182/2011 shall apply.
(*) Regulation (EU) No 182/2011 of the European Parliament and of the Council of 16 February 2011 laying down
the rules and general principles concerning mechanisms for control by Member States of the Commission’s
exercise of implementing powers (OJ L 55, 28.2.2011, p. 13, ELI: http://data.europa.eu/eli/reg/2011/182/oj).’;
(16) in Article 22, paragraph 4 is replaced by the following:
‘4. The environmental objectives in Article 4, the environmental quality standards set out in Part A of Annex I to
Directive 2008/105/EC and the environmental quality standards for river basin specific pollutants established
pursuant to Article 16(4) of this Directive shall be regarded as environmental quality standards for the purposes of
Directive 2010/75/EU.’;
(17) Annex V is amended in accordance with Annex I to this Directive;
(18) in Part B of Annex VII, the following point is added:
‘5. a summary of any measures adopted to take into account the suggestions for improvement made by the
Commission, in accordance with Article 18(2)(c), to the previous plan.’;
(19) Annex VIII is amended in accordance with Annex II to this Directive;
(20) Annexes IX and X are deleted.
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Article 2
Amendments to Directive 2006/118/EC
Directive 2006/118/EC is amended as follows:
(1) the title is replaced by the following
‘Directive 2006/118/EC of the European Parliament and of the Council of 12 December 2006 on the prevention and
control of groundwater pollution’;
(2) in Article 1, paragraph 1 is replaced by the following:
‘1. This Directive establishes specific measures as provided for in Article 17 of Directive 2000/60/EC to prevent
and control groundwater pollution with the aim of achieving the environmental objectives set out in Article 4(1)(b) of
that Directive. Those measures include the following:
(a) criteria for the assessment of good groundwater chemical status; and
(b) criteria for the identification and reversal of significant and sustained upward trends and for the definition of
starting points for trend reversals.’;
(3) Article 2 is amended as follows:
(a) point 2) is replaced by the following:
‘2) “threshold value” means a groundwater quality standard established at Union level and listed in Annex II part D
or established by Member States in accordance with Article 3(1)(b);’;
(b) the following point is added:
‘7) “indicator of pollution” means a parameter which can be monitored to give a value that is representative of the
level or concentration of a pollutant or a group of pollutants and thus of the risk posed by them.’;
(4) Article 3 is amended as follows:
(a) in paragraph 1, first subparagraph, the following point is added:
‘(c) threshold values established at Union level listed in Part D of Annex II.’;
(b) the following paragraphs are inserted:
‘1a. The quality standards for the substances numbered 3 to 8 in Annex I to this Directive shall take effect from
22 December 2027, with the aim of achieving good groundwater chemical status in relation to those substances
by 22 December 2039 and preventing deterioration in the chemical status of groundwater bodies in relation to
those substances. For that purpose, Member States shall, by 22 December 2027, establish a supplementary
monitoring programme and, by 22 December 2030, a preliminary programme of measures covering those
substances. A final programme of measures, in accordance with Article 11 of Directive 2000/60/EC, shall be
included in the 2033 river basin management plan produced in accordance with Article 13(7) of that Directive.
Article 4(4) to (9) of Directive 2000/60/EC shall apply mutatis mutandis to the substances referred to in the first
subparagraph of this paragraph. Insofar as the time extensions provided for in Article 4(4) of that Directive are
concerned, they shall be limited to a maximum of one further update of the river basin management plan except in
cases where the natural conditions are such that the objectives cannot be achieved within that period.
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1b. Threshold values established in accordance with Article 3(1)(b) and the threshold values listed in Part D of
Annex II shall take effect from the beginning of the following river basin management plan period after the date
the threshold value was set, with the aim of achieving good groundwater chemical status in relation to the
corresponding substances by the end of that river basin management plan period and of preventing deterioration
in the chemical status of groundwater bodies in relation to those substances.
Article 4(4) to (9) of Directive 2000/60/EC shall apply mutatis mutandis to the substances referred to in the first
subparagraph of this paragraph. Insofar as the time extensions provided for in Article 4(4) of that Directive are
concerned, they shall be limited to a maximum of one further update of the river basin management plan except in
cases where the natural conditions are such that the objectives cannot be achieved within that period.’;
(c) paragraph 2 is replaced by the following:
‘2. Threshold values referred to in paragraph 1(b) may be established at the national level, at the level of the
river basin district or the part of the international river basin district falling within the territory of a Member State,
or at the level of a body or a group of bodies of groundwater.
Threshold values referred to in paragraph 1(b) and (c) shall be applied at the level relevant to the occurrence of the
pollutant.’;
(d) paragraph 5 is replaced by the following:
‘5. Member States shall publish all threshold values referred to in paragraph 1(b) of this Article in their river
basin management plans to be produced under Article 13 of Directive 2000/60/EC, together with a summary of
the information set out in Part C of Annex II to this Directive.
Member States shall, by 22 December 2027, inform the Commission of their lists of pollutants of national concern
and national threshold values referred to in paragraph 1(b). The Commission shall ensure that that information is
made publicly available. Subsequent updates of the list of national threshold values shall be published in
accordance with the first subparagraph of this paragraph.’;
(e) in paragraph 6, the first subparagraph is replaced by the following:
‘6. Member States shall amend the list of threshold values applied in their territories whenever new information
on pollutants, groups of pollutants or indicators of pollution, also taking into account the precautionary principle,
indicates that a threshold value needs to be set for an additional substance, that an existing threshold value needs
to be modified or that a threshold value previously removed from the list needs to be re-inserted. If relevant
threshold values are established or amended at Union level, Member States shall adapt the list of threshold values
applied in their territories to those values.’;
(5) Article 4 is amended as follows:
(a) in paragraph 2, point (b) is replaced by the following:
‘(b) the values for the groundwater quality standards listed in Annex I and the threshold values referred to in
Article 3(1)(b) and (c) are not exceeded at any monitoring point in that body or group of bodies of
groundwater; or’;
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(b) the following paragraph is inserted:
‘2a. The Commission is empowered to adopt an implementing act to establish a list of pesticide metabolites that
may be found in groundwater and for which an assessment of their relevance has been carried out in the Union,
indicating whether they are relevant or not relevant, by 11 May 2028. The list shall not include metabolites
assessed as being of no concern. The list shall be based on data generated during the process for approving active
substances under Regulation (EC) No 1107/2009 of the European Parliament and of the Council(*) and
Regulation (EU) No 528/2012 of the European Parliament and of the Council(**)and associated scientific output
from the European Food Safety Authority (EFSA) and the European Chemicals Agency (ECHA), and, if available,
new scientific data on existing metabolites or newly discovered previously unidentified metabolites. The
Commission shall adopt an implementing act to update the list at least every six years. The implementing acts
referred to in this paragraph shall be adopted in accordance with the examination procedure referred to in
Article 9(2) of this Directive.
(*) Regulation (EC) No 1107/2009 of the European Parliament and of the Council of 21 October 2009
concerning the placing of plant protection products on the market and repealing Council Directives
79/117/EEC and 91/414/EEC (OJ L 309, 24.11.2009, p. 1, ELI: http://data.europa.eu/eli/reg/2009/1107/oj).
(**) Regulation (EU) No 528/2012 of the European Parliament and of the Council of 22 May 2012 concerning
the making available on the market and use of biocidal products (OJ L 167, 27.6.2012, p. 1, ELI: http://data.
europa.eu/eli/reg/2012/528/oj).’;
(6) the following Article is inserted:
‘Article 6a
Watch list
1. The Commission is empowered to adopt implementing acts to establish, having regard to scientific reports
prepared by ECHA in accordance with paragraph 2 of this Article, a watch list of substances for which Union-wide
monitoring data are to be gathered by the Member States for the purpose of supporting future reviews of
Annexes I and II and to lay down the formats to be used by the Member States for reporting the results of that
monitoring and related information to the Commission. Those implementing acts shall be adopted in accordance with
the examination procedure referred to in Article 9(2).
The watch list shall contain a maximum of five substances, groups of substances, or indicators of pollution at any one
time, and the possible methods of analysis for each substance. Those methods shall not entail excessive costs for the
competent authorities. The substances to be included in the watch list shall be selected from amongst those substances
for which the information available indicates that they could pose a significant risk at Union level to or via the aquatic
environment and for which monitoring data are insufficient. This watch list shall include substances of emerging
concern.
On the basis of the scientific reports prepared by ECHA in accordance with paragraph 2, the Commission shall include
microplastics and appropriate indicators of the presence, evolution or transmission of antimicrobial resistance
(“indicators of antimicrobial resistance”) in the watch list, provided that methods of sampling and analysis that are
reliable and do not entail excessive cost are available. By 1 December 2027 the Commission shall identify such
methods of sampling and analysis.
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2. ECHA shall prepare scientific reports to assist the Commission in selecting the substances, and indicators for
inclusion in the watch list referred to in paragraph 1 of this Article, taking into account the following information:
(a) Annex I to Directive 2008/105/EC of the European Parliament and of the Council(1)*and the results of the most
recent review of that Annex, as well as the results of the most recent review of Annex I to this Directive;
(b) the watch lists established in accordance with Directives 2008/105/EC and (EU) 2020/2184;
(c) requirements to address soil pollution, including related monitoring data;
(d) Member States’ characterisation of river basin districts in accordance with Article 5 of Directive 2000/60/EC and
the results of monitoring programmes established in accordance with Article 8 of that Directive;
(e) information on production volumes, use patterns, intrinsic properties (including mobility in soils and, where
relevant, particle size), concentrations in the environment and adverse effects on human health and the aquatic
environment of a particular substance or group of substances, including information gathered in accordance with
Directive 2001/83/EC of the European Parliament and of the Council(2)*, Regulations (EC) No 1907/2006(3)*and
(EC) No 1107/2009, Directive 2009/128/EC of the European Parliament and of the Council(4)*and Regulations
(EU) No 528/2012, (EU) 2019/6(5)* and (EU) 2022/2379(6)* of the European Parliament and of the Council;
(f) research projects and scientific publications, including, information on trends, and forecasts based on modelling or
other predictive assessments, as well as information and data collected by remote sensing technologies, earth
observation, such as Copernicus services, in situ sensors and devices, or citizen science data, taking advantage of
the opportunities offered by artificial intelligence and advanced data analysis and processing;
(g) recommendations from stakeholders;
(h) recommendations from the working groups established under the Common Implementation Strategy for Directive
2000/60/EC;
(i) information on emissions, discharges and losses available in the Industrial Emissions Portal under Regulation (EU)
2024/1244 of the European Parliament and of the Council(7)*, as well as any additional information available on
substances covered by permits under Directive 2010/75/EU of the European Parliament and of the Council(8)*.
3. The scientific reports prepared by ECHA in accordance with paragraph 2 shall present a list of candidate
substances, groups of substances, or indicators, an indicative method of analysis and maximum acceptable limit of
quantification for each of them, with a supporting reference to scientific literature or guidance.
4. By 1 February 2028 and every three years thereafter, ECHA shall prepare a report summarising the findings of
the scientific reports prepared in accordance with paragraph 2 and shall make that report publicly available. .
5. By 1 June 2028, the Commission shall establish the first watch list referred to in paragraph 1, and update it every
three years thereafter.
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When updating the watch list, the Commission shall remove any substance, group of substances, or indicator from the
watch list, where the Commission considers it possible to assess the risk for the aquatic environment without
additional monitoring data. However, an individual substance, group of substances, or indicator may be kept on the
watch list for another period of three years where additional monitoring data are needed to assess the risk to the
aquatic environment.
The Commission may also add one or more additional substances, groups of substances, or indicators where it
considers, having regard to the scientific reports of ECHA, that there could be a widespread risk to the aquatic
environment, subject to the updated watch list containing a maximum of five substances, groups of substances, or
indicators, in accordance with paragraph 1.
Microplastics and indicators of antimicrobial resistance shall not be kept on the watch list for a second consecutive
period of three years unless a harmonised and reliable risk assessment methodology is available which, when applied,
shows that the monitoring data collected during the first monitoring period are insufficient to assess the risk they pose
to or via the aquatic environment.
6. Member States shall monitor each substance, group of substances, and indicator on the watch list referred to in
paragraph 1 at selected representative monitoring stations over a 24-month period. The monitoring period shall
commence within six months of the establishment of the watch list, but sampling and analysis need not commence at
the start of that period.
Each Member State shall select at least two monitoring stations, plus the number of stations equal to its total area in
km2 of groundwater bodies divided by 45 000, rounded to the nearest integer.
In selecting the representative monitoring stations, the monitoring frequency and the timing for each substance, group
of substances, or indicator, Member States shall take into account seasonal variability in rainfall, water levels, use
patterns and the possibility of the substance, group of substances, or indicator occurring. The frequency of monitoring
shall be not less than once per year.
Where a Member State is in a position to generate sufficient, comparable, representative and recent monitoring data
for a particular substance, group of substances, or indicator from existing monitoring programmes or studies, it may
decide not to undertake additional monitoring under the watch list mechanism for that substance, group of
substances, or indicator, provided that the substance, group of substances, or indicator was monitored using
a methodology that is compliant with the methods of analysis referred to in the implementing act establishing the
watch list.
7. Member States shall make available the results of the monitoring referred to in paragraph 6 of this Article
annually in accordance with Article 8(4) of Directive 2000/60/EC and with the implementing act establishing the
watch list as adopted pursuant to paragraph 1 of this Article. They shall also make available information on the
representativeness of the monitoring stations and on the monitoring strategy.
8. At the end of the 24-month period referred to in paragraph 6 ECHA shall review the monitoring results and
assess which substances, groups of substances, or indicators need to be monitored for another 24-month period and
therefore are to be kept on the watch list and which substances, groups of substances, or indicators can be removed
from the watch list.
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Where the Commission, having regard to the assessment by ECHA referred to in the first subparagraph of this
paragraph, concludes that no further monitoring is required to further assess the risk to the aquatic environment, that
assessment shall be taken into account in the review of Annex I or II referred to in Article 8.
(1)* Directive 2008/105/EC of the European Parliament and of the Council of 16 December 2008 on environmental
quality standards in the field of water policy, amending and subsequently repealing Council Directives
82/176/EEC, 83/513/EEC, 84/156/EEC, 84/491/EEC, 86/280/EEC and amending Directive 2000/60/EC of the
European Parliament and of the Council (OJ L 348, 24.12.2008, p. 84, ELI: http://data.europa.eu/eli/dir/2008/
105/oj).
(2)* Directive 2001/83/EC of the European Parliament and of the Council of 6 November 2001 on the Community
code relating to medicinal products for human use (OJ L 311, 28.11.2001, p. 67, ELI: http://data.europa.eu/eli/
dir/2001/83/oj).
(3)* Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006
concerning the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH), establishing
a European Chemicals Agency, amending Directive 1999/45/EC and repealing Council Regulation (EEC)
No 793/93 and Commission Regulation (EC) No 1488/94 as well as Council Directive 76/769/EEC and
Commission Directives 91/155/EEC, 93/67/EEC, 93/105/EC and 2000/21/EC (OJ L 396, 30.12.2006, p. 1,
ELI: http://data.europa.eu/eli/reg/2006/1907/oj).
(4)* Directive 2009/128/EC of the European Parliament and of the Council of 21 October 2009 establishing
a framework for Community action to achieve the sustainable use of pesticides, (OJ L 309, 24.11.2009, p. 71,
ELI: http://data.europa.eu/eli/dir/2009/128/oj).
(5)* Regulation (EU) 2019/6 of the European Parliament and of the Council of 11 December 2018 on veterinary
medicinal products and repealing Directive 2001/82/EC (OJ L 4, 7.1.2019, p. 43, ELI: http://data.europa.eu/eli/
reg/2019/6/oj).
(6)* Regulation (EU) 2022/2379 of the European Parliament and of the Council of 23 November 2022 on statistics
on agricultural input and output, amending Commission Regulation (EC) No 617/2008 and repealing
Regulations (EC) No 1165/2008, (EC) No 543/2009 and (EC) No 1185/2009 of the European Parliament and of
the Council and Council Directive 96/16/EC (OJ L 315, 7.12.2022, p. 1, ELI: http://data.europa.eu/eli/reg/2022/
2379/oj).
(7)* Regulation (EU) 2024/1244 of the European Parliament and of the Council of 24 April 2024 on reporting of
environmental data from industrial installations, establishing an Industrial Emissions Portal and repealing
Regulation (EC) No 166/2006 (OJ L, 2024/1244, 2.5.2024, ELI: http://data.europa.eu/eli/reg/2024/1244/oj).
(8)* Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial and
livestock rearing emissions (integrated pollution prevention and control) (OJ L 334, 17.12.2010, p. 17,
ELI: http://data.europa.eu/eli/dir/2010/75/oj).’;
(7) Article 8 is replaced by the following:
‘Article 8
Review of Annexes I to IV and specific provisions for certain substances
1. The Commission shall review the list of pollutants and indicators of pollution and the corresponding quality
standards for those pollutants set out in Annex I by 11 May 2032 and every six years thereafter and, where
appropriate, accompany the review with a legislative proposal to update the list of pollutants and the corresponding
quality standards.
2. The Commission shall review the list of pollutants and indicators of pollution for which Member States have to
consider establishing national threshold values set out in Part B of Annex II by 11 May 2032 and every six years
thereafter and, where appropriate, accompany the review with a legislative proposal to update the list of pollutants in
Part B of Annex II.
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3. The Commission shall review the repository of harmonised threshold values in Part D of Annex II by 11 May
2032 and every six years thereafter and, where appropriate, accompany the review with a legislative proposal to
update the repository and the corresponding harmonised threshold values in Part D of Annex II.
4. When conducting the reviews referred to in paragraphs 1, 2 and 3, the Commission shall take the scientific
reports prepared by ECHA pursuant to paragraph 6 into account.
5. The Commission is empowered to adopt delegated acts in accordance with Article 8a to amend Parts A and C of
Annex II and Annexes III and IV concerning guidelines for the establishment of threshold values by Member States,
information to be provided by Member States with regard to the pollutants and indicators of pollution for which
threshold values have been established, the assessment of groundwater chemical status and the identification and
reversal of significant and sustained upward trends in order to adapt them to scientific and technical progress.
6. For the purpose of assisting the Commission with regard to the review of Annexes I and II, ECHA shall prepare
scientific reports. Those reports shall take account of the following:
(a) the opinions of the Committee for Risk Assessment (RAC) and the Committee for Socio-Economic Analysis
(SEAC) of ECHA;
(b) the results of the monitoring programmes established in accordance with Article 8 of Directive 2000/60/EC;
(c) the review of the monitoring results in accordance with Article 6a(8) of this Directive;
(d) the outcome of the reviews of the Annexes to Directive 2008/105/EC and Directive (EU) 2020/2184;
(e) information and requirements to address soil pollution;
(f) Union research programmes and scientific publications, including the latest available information resulting from
remote sensing technologies, earth observation, such as Copernicus services, in situ sensors and devices and citizen
science data, leveraging the opportunities offered by new technologies, which could include artificial intelligence,
advanced data analysis and processing;
(g) comments and information from relevant stakeholders, including national regulatory authorities and other
relevant bodies;
(h) recommendations from the working groups established under the Common Implementation Strategy for Directive
2000/60/EC.
The scientific reports referred to in the first subparagraph shall include proposals for quality standards or threshold
values for the respective pollutants or indicators of pollution as well as a suitable analytical method.
7. Every six years, ECHA shall prepare and make publicly available a report, summarising the findings of the
scientific reports prepared under paragraph 6. The first report shall be submitted to the Commission by 11 May 2030.
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8. When next conducting the review referred to in paragraph 1 of this Article, the Commission shall consider
establishing a quality standard for PFAS Total in groundwater and aim to complement the guidance on monitoring
PFAS Total in drinking water, developed in accordance with Article 13(7) of Directive (EU) 2020/2184, to make it
applicable to monitoring PFAS Total in groundwater. Member States are encouraged to already apply that guidance to
monitor PFAS Total in groundwater and to report the data in accordance with Article 8(4) of Directive 2000/60/EC.
Considering the toxicity, persistence and prevalence of trifluoroacetic acid (TFA) in the environment, the Commission
shall, at the next review, also consider establishing a quality standard for TFA separately, or as a part of a sum, in
Annex I to this Directive.
9. When next conducting the review referred to in paragraph 1, the Commission shall consider whether to
establish quality standards for the sum(s) of selected pharmaceuticals by mode of action and for the sum of bisphenols;
for this reason “sum(s) of selected pharmaceuticals by mode of action” and “sum of bisphenols” are listed in
Annex V to Directive 2006/118/EC. The Commission shall also consider whether a risk-based approach could be
taken to establishing quality standards for total pharmaceuticals and total bisphenols in groundwater, supported by
suitable monitoring methods.
10. When next conducting the review referred to in paragraph 1, the Commission shall consider whether to revise
the quality standards in Annex I for individual pesticides, total pesticides and for non-relevant metabolites in
groundwater.’;
(8) the following Article is inserted:
‘Article 8a
Exercise of the delegation
1. The power to adopt delegated acts is conferred on the Commission subject to the conditions laid down in this
Article.
2. The power to adopt delegated acts referred to in Article 8(5) shall be conferred on the Commission for a period
of six years from 10 May 2026. The Commission shall draw up a report in respect of the delegation of power not later
than nine months before the end of the six-year period. The delegation of power shall be tacitly extended for periods
of an identical duration, unless the European Parliament or the Council opposes such extension not later than three
months before the end of each period.
3. The delegation of power referred to in Article 8(5) may be revoked at any time by the European Parliament or by
the Council. A decision to revoke shall put an end to the delegation of the power specified in that decision. It shall take
effect the day following the publication of the decision in the Official Journal of the European Union or at a later date
specified therein. It shall not affect the validity of the delegated acts already in force.
4. Before adopting a delegated act, the Commission shall consult experts designated by each Member State in
accordance with the principles laid down in the Interinstitutional Agreement of 13 April 2016 on Better Law-Making.
5. As soon as it adopts a delegated act, the Commission shall notify it simultaneously to the European Parliament
and to the Council.
6. A delegated act adopted pursuant to Article 8(5) shall enter into force only if no objection has been expressed
either by the European Parliament or by the Council within a period of two months of notification of that act to the
European Parliament and the Council or if, before the expiry of that period, the European Parliament and the Council
have both informed the Commission that they will not object. That period shall be extended by two months at the
initiative of the European Parliament or of the Council.’;
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(9) Article 9 is replaced by the following:
‘Article 9
Committee procedure
1. The Commission shall be assisted by a committee. That committee shall be a committee within the meaning of
Regulation (EU) No 182/2011 of the European Parliament and of the Council(*).
2. Where reference is made to this paragraph, Article 5 of Regulation (EU) No 182/2011 shall apply.
Where the committee delivers no opinion, the Commission shall not adopt the draft implementing act and
Article 5(4), third subparagraph, of Regulation (EU) No 182/2011 shall apply.
(*) Regulation (EU) No 182/2011 of the European Parliament and of the Council of 16 February 2011 laying down
the rules and general principles concerning mechanisms for control by Member States of the Commission’s
exercise of implementing powers (OJ L 55, 28.2.2011, p. 13, ELI: http://data.europa.eu/eli/reg/2011/182/oj).’;
(10) Article 10 is deleted;
(11) Annex I is replaced by the text set out in Annex III to this Directive;
(12) Annex II is amended in accordance with Annex IV to this Directive;
(13) in Annex III, point 2(c) is replaced by the following:
‘(c) any other relevant information including a comparison of the annual arithmetic mean concentration of the
relevant pollutants at a monitoring point with the groundwater quality standards set out in Annex I and with the
threshold values referred to in Article 3(1)(b) and (c).’;
(14) in Annex IV, Part B, point 1, the introductory wording is replaced by the following:
‘1) the starting point for implementing measures to reverse significant and sustained upward trends will be when the
concentration of the pollutant reaches 75 % of the parametric values of the groundwater quality standards set out
in Annex I and of the threshold values referred to in Article 3(1)(b) and (c), unless:’;
(15) the text set out in Annex V of this Directive is added as Annex V.
Article 3
Amendments to Directive 2008/105/EC
Directive 2008/105/EC is amended as follows:
(1) the title is replaced by the following:
‘Directive 2008/105/EC of the European Parliament and of the Council of 16 December 2008 on environmental
quality standards and on the prevention and control of surface water pollution, amending and subsequently repealing
Council Directives 82/176/EEC, 83/513/EEC, 84/156/EEC, 84/491/EEC, 86/280/EEC and amending Directive
2000/60/EC of the European Parliament and of the Council’;
(2) in Article 2 the following point is added:
‘(3) “indicator of pollution” means a parameter which can be monitored to give a value that is representative of the
level or concentration of a pollutant or a group of pollutants and thus of the risk posed by them.’;
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(3) Article 3 is amended as follows:
(a) paragraph 1a is amended as follows:
(i) in the first subparagraph, the following points are added:
‘(iii) the substances numbered 5, 9, 13, 15, 17, 21, 23, 24, 28, 30, 34, 37, 41 and 43 in Part A of Annex I, for
which revised EQS are set, with effect from 22 December 2027, with the aim of achieving good surface
water chemical status in relation to those substances by 22 December 2033 and preventing deterioration
in the chemical status of surface water bodies in relation to those substances by means of programmes of
measures included in the 2027 river basin management plans produced in accordance with Article 13(7)
of Directive 2000/60/EC;
(iv) the newly identified substances numbered 46 to 70 in Part A of Annex I, with effect from 22 December
2027, with the aim of achieving good surface water chemical status in relation to those substances
by 22 December 2039 and preventing deterioration in the chemical status of surface water bodies in
relation to those substances; for that purpose, Member States shall, by 22 December 2027, establish
a supplementary monitoring programme and, by 22 December 2030, a preliminary programme of
measures covering those substances; a final programme of measures, in accordance with Article 11 of
Directive 2000/60/EC, shall be included in the 2033 river basin management plan produced in
accordance with Article 13(7) of that Directive.’;
(ii) the second subparagraph is replaced by the following:
‘Article 4(4) to (9) of Directive 2000/60/EC shall apply mutatis mutandis to the substances listed in points (i) and
(ii), of the first subparagraph of this paragraph.
Article 4(4) to (9) of Directive 2000/60/EC shall also apply mutatis mutandis to the substances listed in points
(iii) and (iv) of the first subparagraph of this paragraph. Insofar as the time extensions provided for in
Article 4(4) of that Directive are concerned, they shall be limited to a maximum of one further update of the
river basin management plan except in cases where the natural conditions are such that the objectives cannot
be achieved within that river basin management plan period.’;
(b) the following paragraph is added:
‘1b. EQS set at Union level for river basin specific pollutants in accordance with Article 16(4) of Directive
2000/60/EC and listed in Part C of Annex II to this Directive or additional river basin specific pollutants and
corresponding EQS identified by Member States in accordance with Article 8d(1) of this Directive, shall take effect
from the beginning of the following river basin management plan period after the date the EQS was set, with the
aim of achieving good surface water chemical status in relation to those pollutants by the end of that river basin
management plan period and of preventing deterioration in the chemical status of surface water bodies in relation
to those pollutants.
Article 4(4) to (9) of Directive 2000/60/EC shall apply mutatis mutandis to the pollutants referred to in the first
subparagraph of this paragraph. Insofar as the time extensions provided for in Article 4(4) of that Directive are
concerned, they shall be limited to a maximum of one further update of the river basin management plan except in
cases where the natural conditions are such that the objectives cannot be achieved within that river basin
management plan period.’;
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(c) paragraph 2 is replaced by the following:
‘2. With regard to substances for which a biota EQS or a sediment EQS is laid down in Part A of Annex I,
Member States shall apply such biota EQS or sediment EQS.
With regard to substances other than those referred to in the first subparagraph, Member States shall apply the
water EQS laid down in Part A of Annex I.’;
(d) in paragraph 6, the first subparagraph is replaced by the following:
‘6. Member States shall arrange for the long-term trend analysis of concentrations of those priority substances
identified in Part A of Annex I as substances that tend to accumulate in sediment or biota, on the basis of
monitoring in sediment or biota as part of the monitoring of surface water status carried out in accordance with
Article 8 of Directive 2000/60/EC. Member States shall take measures aimed at ensuring, subject to Article 4 of
Directive 2000/60/EC, that such concentrations do not significantly increase in sediment or biota.’;
(e) paragraph 7 is deleted;
(f) paragraph 8 is replaced by the following:
‘8. The Commission is empowered to adopt delegated acts in accordance with Article 9a to amend point 3 of
Part B of Annex I in order to adapt it to scientific or technical progress.’;
(4) Article 5 is replaced by the following:
‘Article 5
Inventory of emissions, discharges and losses
1. On the basis of the information collected in accordance with Articles 5 and 8 of Directive 2000/60/EC and other
available data, each Member State shall establish an inventory of emissions, discharges and losses of all priority
substances listed in Part A of Annex I to this Directive and all substances identified by the Member State as river basin
specific pollutants for each river basin district or part of a river basin district within their territory.
The first subparagraph shall not apply to emissions, discharges and losses reported by electronic means, on a yearly
basis, to the Industrial Emissions Portal established under Regulation (EU) 2024/1244 of the European Parliament and
of the Council(*), in accordance with Article 7 of that Regulation.
2. Member States shall update their inventories as part of the reviews specified in Article 5(2) of Directive
2000/60/EC.
The reference period for the establishment of values in the updated inventories shall be the year before the year in
which the reviews specified in Article 5(2) of Directive 2000/60/EC are to be completed.
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As part of those updates, Member States shall ensure that the point source emissions to water that do not fall under
the scope of Regulation (EU) 2024/1244 or that fall below the annual reporting thresholds set out in that Regulation,
as well as the emissions of pollutants from diffuse sources as defined in point (12) of Article 3 of that Regulation, to
water, are also reported by electronic means to the Commission, in order to be made available in the Industrial
Emissions Portal established under that Regulation, at least every six years, and aggregated at the level of each river
basin district or part thereof within a Member State’s territory.
The Commission shall adopt an implementing act establishing the format of the reporting referred to in the third
subparagraph of this paragraph. That implementing act shall be adopted in accordance with the examination
procedure referred to in Article 9(2) of this Directive. When establishing that implementing act, the Commission shall
be assisted, where so required, by the EEA.
3. Member States shall ensure that the river basin management plans established in accordance with Article 13 of
Directive 2000/60/EC include a clear reference or weblink to all the information on emissions to water made available
in the Industrial Emissions Portal in accordance with paragraphs 1 and 4 of this Article.
(*) Regulation (EU) 2024/1244 of the European Parliament and of the Council of 24 April 2024 on reporting of
environmental data from industrial , establishing an Industrial Emissions Portal and repealing Regulation (EC)
No 166/2006 (OJ L, 2024/1244, 2.5.2024, ELI: http://data.europa.eu/eli/reg/2024/1244/oj).’;
(5) in Article 7a, paragraph 1 is replaced by the following:
‘1. For priority substances that fall within the scope of Directive 2001/83/EC of the European Parliament and of the
Council(1)*, Regulations (EC) No 1907/2006(2)* or (EC) No 1107/2009(3)* of the European Parliament and of the
Council, Directives 2009/128/EC(4)* or 2010/75/EU(5)* of the European Parliament and of the Council or
Regulations (EU) No 528/2012(6)* or (EU) 2019/6 of the European Parliament and of the Council(7)*, the
Commission shall, taking into account the monitoring data referred to in Article 8(4) of Directive 2000/60/EC, and as
part of the report referred to in Article 18(1) of that Directive, assess whether the measures in place at Union and
Member State level are sufficient to achieve the EQS for priority substances and the cessation or phasing-out objective
for discharges, emissions and losses of priority hazardous substances in accordance with point (a) of Article 4(1) of
Directive 2000/60/EC.
(1)* Directive 2001/83/EC of the European Parliament and of the Council of 6 November 2001 on the Community
code relating to medicinal products for human use (OJ L 311, 28.11.2001, p. 67, ELI: http://data.europa.eu/eli/
dir/2001/83/oj).
(2)* Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006
concerning the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH), establishing
a European Chemicals Agency, amending Directive 1999/45/EC and repealing Council Regulation (EEC)
No 793/93 and Commission Regulation (EC) No 1488/94 as well as Council Directive 76/769/EEC and
Commission Directives 91/155/EEC, 93/67/EEC, 93/105/EC and 2000/21/EC (OJ L 396, 30.12.2006, p. 1,
ELI: http://data.europa.eu/eli/reg/2006/1907/oj).
(3)* Regulation (EC) No 1107/2009 of the European Parliament and of the Council of 21 October 2009 concerning
the placing of plant protection products on the market and repealing Council Directives 79/117/EEC and
91/414/EEC (OJ L 309, 24.11.2009, p. 1, ELI: http://data.europa.eu/eli/reg/2009/1107/oj).
(4)* Directive 2009/128/EC of the European Parliament and of the Council of 21 October 2009 establishing
a framework for Community action to achieve the sustainable use of pesticides, (OJ L 309, 24.11.2009, p. 71,
ELI: http://data.europa.eu/eli/dir/2009/128/oj).
(5)* Directive 2010/75/EU of the European Parliament and of the Council of 24 November 2010 on industrial and
livestock rearing emissions (integrated pollution prevention and control) (OJ L 334, 17.12.2010, p. 17,
ELI: http://data.europa.eu/eli/dir/2010/75/oj).
(6)* Regulation (EU) No 528/2012 of the European Parliament and of the Council of 22 May 2012 concerning the
making available on the market and use of biocidal products (OJ L 167, 27.6.2012, p. 1, ELI: http://data.europa.
eu/eli/reg/2012/528/oj).
(7)* Regulation (EU) 2019/6 of the European Parliament and of the Council of 11 December 2018 on veterinary
medicinal products and repealing Directive 2001/82/EC (OJ L 4, 7.1.2019, p. 43, ELI: http://data.europa.eu/eli/
reg/2019/6/oj).’;
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(6) Articles 8, 8a and 8b are replaced by the following:
‘Article 8
Review of Annexes I and II
1. The Commission shall consider establishing quality standards for PFAS Total in surface waters at the next review
of Annex I to this Directive to be conducted in accordance with Article 16 of Directive 2000/60/EC and aim to
complement the guidance on monitoring PFAS Total in drinking water, developed in accordance with Article 13(7) of
Directive (EU) 2020/2184 of the European Parliament and of the Council(*), to make it applicable to monitoring PFAS
Total in surface waters. Member States are encouraged to already apply that guidance to monitor PFAS Total in surface
waters and to report the data in line with Article 8(4) of Directive 2000/60/EC. Considering the toxicity, persistence
and prevalence of trifluoroacetic acid (TFA) in the environment, the Commission shall consider establishing a quality
standard for TFA separately in Annex I to this Directive at the next review.
2. A parameter “Sum of Bisphenols” and parameters for the sum(s) of selected pesticides by mode of action and
selected pharmaceuticals by mode of action are included in Annex III to this Directive. The Commission shall review
the possible inclusion of these parameters in the priority substances list at its next review of Annex I to this Directive
to be conducted in accordance with Article 16 of Directive 2000/60/EC, and set EQS as appropriate. The Commission
shall also consider at the next review whether a risk-based approach could be taken to establishing EQS for total
bisphenols, total pesticides and total pharmaceuticals in surface waters, supported by suitable monitoring methods.
3. The Commission is empowered to adopt delegated acts, in accordance with Article 9a, to amend Part B of
Annex II in order to adapt it to scientific and technological progress.
Article 8a
Specific provisions for certain substances
1. In the river basin management plans produced in accordance with Article 13 of Directive 2000/60/EC, without
prejudice to the requirements of Section 1.4.3 of Annex V to that Directive regarding the presentation of the overall
chemical status and the objectives and obligations laid down in point (a) of Article 4(1), point (k) of Article 11(3) and
in Article 16(6) of that Directive, Member States may provide additional maps to present the chemical status as
provided for in Section 1.4.3 of Annex V of Directive 2000/60/EC.
2. Member States may monitor substances identified in Part A of Annex I to this Directive as substances behaving
like ubiquitous PBTs less intensively than is required for priority substances in accordance with Article 3(4) of this
Directive and Annex V to Directive 2000/60/EC, provided that the monitoring is representative and a statistically
robust baseline is available regarding the presence of those substances in the aquatic environment. As a guideline, in
accordance with the second subparagraph of Article 3(6) of this Directive, monitoring should take place at least every
three years, unless the use or emission of the substance, or technical knowledge and expert judgment, justify another
interval.
3. Over a period of two years from 1 January 2030, Member States shall monitor the presence of estrogenic
substances in water bodies, using effect-based monitoring methods. Sampling and analysis need not commence at the
start of that two-year period, but shall be conducted at least four times each year. Member States shall conduct the
monitoring at a selection of the sites where the three estrogenic hormones 17-beta estradiol (E2), Estrone (E1) and
17-alpha-ethinylestradiol (EE2), listed in Part A to Annex I to this Directive, are being monitored using conventional
analytical methods in accordance with Article 8 of Directive 2000/60/EC and Annex V thereto in order to obtain
comparative results at a range of concentrations. Data shall be reported together, and in accordance with Article 8(4)
of that Directive. The number of sites shall be no fewer than that specified in Article 8b(3) of this Directive for
monitoring substances on the watch list. Member States may start the monitoring before 1 January 2030 as long as
the technical specifications referred to in paragraph 4 of this Article have been adopted. Member States shall not use
the effect-based results from the two-year comparative monitoring period for the purpose of classifying the chemical
status of the monitored water bodies as described in Section 1.4.3 of Annex V to Directive 2000/60/EC.
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4. By 1 December 2027, the Commission shall adopt an implementing act setting out the technical specifications
for the monitoring of estrogenic substances using effect-based monitoring methods. The implementing act shall be
adopted in accordance with the examination procedure referred to in Article 9(2).
5. Within 18 months of the data being reported by the Member States, the Commission shall publish a report
comparing the results from the conventional analytical and the effect-based methods and analyse the possibility of
using effect-based monitoring methods in conjunction with an effect-based trigger value for estrogens as defined in
point 35a of Article 2 of Directive 2000/60/EC for screening purposes to support the assessment of chemical status.
In the context of future reviews of the list of pollutants in accordance with Article 16(2) of Directive 2000/60/EC,
taking into account the analysis in the report referred to in the first subparagraph of this paragraph, the Commission
shall consider setting a trigger value for estrogens for screening purposes and for the assessment of chemical status.
Once effect-based methods are ready to use also for other substances, the Commission shall consider, in the context of
future reviews, requiring Member States to use them, if necessary, at least initially in parallel with conventional
analytical methods, and consider setting corresponding trigger values.
Article 8b
Watch list
1. The Commission is empowered to adopt implementing acts to establish, having regard to scientific reports
prepared by the European Chemicals Agency (ECHA) in accordance with paragraph 1a of this Article, a watch list of
substances for which it is necessary to gather Union-wide monitoring data from the Member States for the purpose of
supporting future reviews in accordance with Article 16(2) of Directive 2000/60/EC and to lay down the formats to be
used by the Member States for reporting the results of that monitoring and related information to the Commission.
Those implementing acts shall be adopted in accordance with the examination procedure referred to in Article 9(2).
The watch list shall contain a maximum of 10 substances, groups of substances, or indicators of pollution at any one
time and shall indicate the monitoring matrices and the possible methods of analysis for each substance. Those
monitoring matrices and methods shall not entail excessive costs for the competent authorities. The substances to be
included in the watch list shall be selected from amongst the substances for which the information available indicates
that they could pose a significant risk at Union level to, or via, the aquatic environment and for which monitoring data
are insufficient. The watch list shall include substances of emerging concern.
On the basis of the scientific reports prepared by ECHA in accordance with paragraph 1a, the Commission shall
include microplastics and appropriate indicators of the presence, evolution or transmission of antimicrobial resistance
(“indicators of antimicrobial resistance”) in the watch list, provided that methods of sampling and analysis that are
reliable and do not entail excessive costs are available. By 1 December 2027, the Commission shall identify such
methods of sampling and analysis.
1a. ECHA shall prepare scientific reports to assist the Commission in selecting the substances and indicators for
inclusion in the watch list referred to in paragraph 1 of this Article, taking into account the following information:
(a) Annex I to Directive 2006/118/EC of the European Parliament and of the Council(*)and the results of the most
recent review of that Annex, as well as the results of the most recent regular review of Annex I to this Directive;
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(b) the watch lists established in accordance with Directives 2006/118/EC and (EU) 2020/2184;
(c) recommendations from the stakeholders;
(d) Member States’ characterisation of river basin districts in accordance with Article 5 of Directive 2000/60/EC and
the results of monitoring programmes established in accordance with Article 8 of that Directive;
(e) information on production volumes, use patterns, intrinsic properties, including, where relevant, particle size,
concentrations in the environment and adverse effects on human health and the aquatic environment of
a substance, including information gathered in accordance with Directive 2001/83/EC, Regulation (EC)
No 1907/2006, Regulation (EC) No 1272/2008 of the European Parliament and of the Council(**), Regulation
(EC) No 1107/2009, Directive 2009/128/EC, Regulation (EU) No 528/2012 and Regulation (EU) 2022/2379 of
the European Parliament and of the Council(***);
(f) research projects and scientific publications, including information on trends and forecasts based on modelling or
other predictive assessments, as well as information and data collected by remote sensing technologies, earth
observation, such as Copernicus services, in situ sensors and devices or citizen science data, taking advantage of
the opportunities offered by artificial intelligence, and advanced data analysis and processing;
(g) recommendations from the working groups established under the Common Implementation Strategy for Directive
2000/60/EC;
(h) information on emissions, discharges and losses available in the Industrial Emissions Portal under Regulation (EU)
2024/1244, as well as any additional information available on substances covered by permits under
Directive 2010/75/EU.
1b. The scientific reports prepared by ECHA in accordance with paragraph 1a shall present a list of substances,
groups of substances, or indicators, the recommended monitoring matrix, and an indicative method of analysis and
maximum acceptable limit of quantification for each of them, with a supporting reference to scientific literature or
guidance.
1c. By 1 February 2028 and every three years thereafter, ECHA shall prepare a report summarising the findings of
the scientific reports prepared in accordance with paragraph 1a and shall make that report publicly available.
2. The Commission shall update the watch list referred to in paragraph 1 by 1 May 2028, and every three years
thereafter.
When updating the watch list, the Commission shall remove any substance or indicator from the watch list for which
a risk-based assessment as referred to in Article 16(2) of Directive 2000/60/EC can be conducted without additional
monitoring data. However, an individual substance, group of substances, or indicator may be kept on the watch list for
another period of maximum three years where additional monitoring data are needed to assess the risk to the aquatic
environment.
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Each updated watch list shall also include one or more additional substances, groups of substances, or indicators for
which the Commission considers, on the basis of the scientific reports of ECHA, that there could be a widespread risk
to or via the aquatic environment, subject to the updated watch list containing a maximum of 10 substances, groups
of substances, or indicators, in accordance with paragraph 1.
Microplastics and indicators of antimicrobial resistance shall not be kept on the list for a second consecutive period of
three years unless a harmonised and reliable risk assessment methodology is available which, when applied, shows
that the monitoring data collected during the first monitoring period are insufficient to assess the risk they pose to or
via the aquatic environment.
3. Member States shall monitor each substance, group of substances, and indicator on the watch list referred to in
paragraph 1 at selected representative monitoring stations over a 24-month period. The monitoring period shall
commence within six months of the inclusion of the substance in the list, but sampling and analysis need not
commence at the start of that period.
Each Member State shall select at least one monitoring station, plus one station if it has more than one million
inhabitants, plus the number of stations equal to its geographical area in km2 divided by 60 000, rounded to the
nearest integer, plus the number of stations equal to its population divided by five million, rounded to the nearest
integer.
In selecting the representative monitoring stations, the monitoring frequency and the timing for each substance, group
of substances, or indicator, Member States shall take into account seasonal variability in rainfall, water levels, use
patterns and the possibility of the substance, group of substances, or indicator occurring. The frequency of monitoring
shall be no less than twice per year when carried out in water and no less than once per year when carried out in
sediment or biota. When higher frequencies are required, as for substances that are sensitive to climatic or seasonal
variabilities, the increase in frequency shall be set out and technically justified in the implementing act establishing the
watch list adopted pursuant to paragraph 1.
Where a Member State is in a position to generate and provide the Commission with sufficient, comparable,
representative and recent monitoring data for a particular substance, group of substances, or indicator from existing
monitoring programmes or studies, it may decide not to undertake additional monitoring under the watch list
mechanism for that substance, group of substances, or indicator, provided that the substance, group of substances, or
indicator was monitored using a methodology that is compliant with the monitoring matrices and the methods of
analysis referred to in the implementing act establishing the watch list, as well as with Commission Directive
2009/90/EC(****).
4. Member States shall make available the results of the monitoring referred to in paragraph 3 of this Article
annually in accordance with Article 8(4) of Directive 2000/60/EC and with the implementing act establishing the
watch list adopted pursuant to paragraph 1 of this Article. They shall also make available information on the
representativeness of the monitoring stations and on the monitoring strategy.
5. At the end of the 24-month period referred to in paragraph 3 ECHA shall review the monitoring results and
assess which substances, groups of substances, or indicators need to be monitored for another 24-month period and
therefore are to be kept on the watch list and which substances, groups of substances, or indicators can be removed
from the watch list.
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Where the Commission, having regard to the assessment by ECHA referred to in the first subparagraph of this
paragraph, concludes that no further monitoring is required to further assess the risk to the aquatic environment, this
assessment by ECHA shall be taken into account in the review of the lists of substances in Annex I or Part C of
Annex II to this Directive, in accordance with Article 16 of Directive 2000/60/EC.
(*) Directive 2006/118/EC of the European Parliament and of the Council of 12 December 2006 on the prevention
and control of groundwater pollution (OJ L 372, 27.12.2006, p. 19, ELI: http://data.europa.eu/eli/dir/2006/118/
oj).
(**) Regulation (EC) No 1272/2008 of the European Parliament and of the Council of 16 December 2008 on
classification, labelling and packaging of substances and mixtures, amending and repealing Directives
67/548/EEC and 1999/45/EC, and amending Regulation (EC) No 1907/2006 (OJ L 353, 31.12.2008, p. 1,
ELI: http://data.europa.eu/eli/reg/2008/1272/oj).
(***) Regulation (EU) 2022/2379 of the European Parliament and of the Council of 23 November 2022 on statistics
on agricultural input and output, amending Commission Regulation (EC) No 617/2008 and repealing
Regulations (EC) No 1165/2008, (EC) No 543/2009 and (EC) No 1185/2009 of the European Parliament and of
the Council and Council Directive 96/16/EC (OJ L 315, 7.12.2022, p. 1, ELI: http://data.europa.eu/eli/reg/2022/
2379/oj).
(****)Commission Directive 2009/90/EC of 31 July 2009 laying down, pursuant to Directive 2000/60/EC of the
European Parliament and of the Council, technical specifications for chemical analysis and monitoring of water
status (OJ L 201, 1.8.2009, p. 36, ELI: http://data.europa.eu/eli/dir/2009/90/oj).’;
(7) the following Article is inserted:
‘Article 8d
River basin specific pollutants
1. Member States shall set and apply EQS for the river basin specific pollutants covered by the categories listed in
Part A of Annex II to this Directive, where they identify those pollutants as posing a risk to water bodies in one or
more of their river basin districts based on the analyses and reviews under Article 5 of Directive 2000/60/EC, in
accordance with the procedure set out in Part B of Annex II to this Directive.
By 22 December 2027, Member States shall inform the Commission of their list of river basin specific pollutants and
EQS set pursuant to the first subparagraph of this paragraph. The Commission shall ensure that that information is
made publicly available.
Subsequent updates of the list of river basin specific pollutants identified by the Member States in accordance with the
first subparagraph of this paragraph and their corresponding EQS shall be included in the river basin management
plans to be produced under Article 13 of Directive 2000/60/EC.
2. Where EQS for river basin specific pollutants have been set at Union level in accordance with Article 16(4) of
Directive 2000/60/EC, and listed in Part C of Annex II to this Directive, those EQS shall take precedence over EQS for
river basin specific pollutants established at national level in accordance with paragraph 1 of this Article. Those EQS
set at Union level shall also be applied by the Member States to establish whether the river basin specific pollutants
listed in Part C of Annex II to this Directive pose a risk.
3. Compliance with the applicable national EQS or, where relevant, with the EQS set at Union level, is required for
a water body to achieve good surface water chemical status, as defined in point 24 of Article 2 of Directive
2000/60/EC.’;
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(8) Article 9a is amended as follows:
(a) paragraphs 2 and 3 are replaced by the following:
‘2. The power to adopt delegated acts referred to in Article 3(8) and Article 8(3) shall be conferred on the
Commission for a period of six years from 10 May 2026. The Commission shall draw up a report in respect of the
delegation of power at the latest nine months before the end of the six-year period. The delegation of power shall
be tacitly extended for periods of an identical duration, unless the European Parliament or the Council opposes
such extension not later than three months before the end of each period.
3. The delegation of power referred to in Article 3(8) and Article 8(3) may be revoked at any time by the
European Parliament or by the Council. A decision to revoke shall put an end to the delegation of the power
specified in that decision. It shall take effect the day following the publication of the decision in the Official Journal
of the European Union or at a later date specified therein. It shall not affect the validity of any delegated acts already
in force.
3a. Before adopting a delegated act, the Commission shall consult experts designated by each Member State in
accordance with the principles laid down in the Interinstitutional Agreement of 13 April 2016 on Better
Law-Making.’;
(b) paragraph 5 is replaced by the following:
‘5. A delegated act adopted pursuant to Article 3(8) or Article 8(3) shall enter into force only if no objection has
been expressed either by the European Parliament or the Council within a period of two months of notification of
that act to the European Parliament and the Council or if, before the expiry of that period, the European Parliament
and the Council have both informed the Commission that they will not object. That period shall be extended by
two months at the initiative of the European Parliament or of the Council.’;
(9) Article 10 is deleted;
(10) Annex I is amended in accordance with Annex VI to this Directive;
(11) the text set out in Annex VII to this Directive is added as Annex II;
(12) the text set out in Annex VIII to this Directive is added as Annex III.
Article 4
Transposition
1. Member States shall bring into force the laws, regulations and administrative provisions necessary to comply with this
Directive by 21 December 2027. They shall immediately communicate the text of those measures to the Commission.
When Member States adopt those measures, they shall contain a reference to this Directive or be accompanied by such
a reference on the occasion of their official publication. They shall determine how such reference is to be made.
2. Member States shall communicate to the Commission the text of the main measures of national law which they adopt
in the field covered by this Directive.
Article 5
Entry into force
This Directive shall enter into force on the twentieth day following that of its publication in the Official Journal of the
European Union.
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Article 6
Addressees
This Directive is addressed to the Member States.
Done at Brussels, 30 March 2026.
For the European Parliament For the Council
The President The President
R. METSOLA M. PANAYIOTOU
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ANNEX I
Annex V to Directive 2000/60/EC is amended as follows:
(1) Sections 1.1.1 to 1.1.4 are replaced by the following:
‘1.1.1. Rivers
Biological elements
Composition and abundance of aquatic flora
Composition and abundance of benthic invertebrate fauna
Composition, abundance and age structure of fish fauna
Hydromorphological elements supporting the biological elements
Hydrological regime
quantity and dynamics of water flow
connection to groundwater bodies
River continuity
Morphological conditions
river depth and width variation
structure and substrate of the river bed
structure of the riparian zone
General physico-chemical elements supporting the biological elements
Thermal conditions
Oxygenation conditions
Salinity
Acidification status
Nutrient conditions
1.1.2. Lakes
Biological elements
Composition, abundance and biomass of phytoplankton
Composition and abundance of other aquatic flora
Composition and abundance of benthic invertebrate fauna
Composition, abundance and age structure of fish fauna
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Hydromorphological elements supporting the biological elements
Hydrological regime
quantity and dynamics of water flow
residence time
connection to the groundwater body
Morphological conditions
lake depth variation
quantity, structure and substrate of the lake bed
structure of the lake shore
General physico-chemical elements supporting the biological elements
Transparency
Thermal conditions
Oxygenation conditions
Salinity
Acidification status
Nutrient conditions
1.1.3. Transitional waters
Biological elements
Composition, abundance and biomass of phytoplankton
Composition and abundance of other aquatic flora
Composition and abundance of benthic invertebrate fauna
Composition and abundance of fish fauna
Hydro-morphological elements supporting the biological elements
Morphological conditions
depth variation
quantity, structure and substrate of the bed
structure of the intertidal zone
Tidal regime
freshwater flow
wave exposure
General physico-chemical elements supporting the biological elements
Transparency
Thermal conditions
Oxygenation conditions
Salinity
Nutrient conditions
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1.1.4. Coastal waters
Biological elements
Composition, abundance and biomass of phytoplankton
Composition and abundance of other aquatic flora
Composition and abundance of benthic invertebrate fauna
Hydromorphological elements supporting the biological elements
Morphological conditions
depth variation
structure and substrate of the coastal bed
structure of the intertidal zone
Tidal regime
direction of dominant currents
wave exposure
General physico-chemical elements supporting the biological elements
Transparency
Thermal conditions
Oxygenation conditions
Salinity
Nutrient conditions’;
46/84 ELI: http://data.europa.eu/eli/dir/2026/805/oj(2) in Section 1.2.1, the table ‘Physico-chemical quality elements’ is replaced by the following:
‘General physico-chemical quality elements
Element High status Good status Moderate status
General conditions The values of the general physico-chemical Temperature, oxygen balance, pH, acid Conditions consistent with the achievement of
elements correspond totally or nearly totally neutralising capacity and salinity do not the values specified above for the biological
to undisturbed conditions. reach levels outside the ranges established so quality elements.’;
as to ensure the functioning of the type
Nutrient concentrations remain within the
specific ecosystem and the achievement of
range normally associated with undisturbed
the values specified above for the biological
conditions.
quality elements.
Levels of salinity, pH, oxygen balance, acid
Nutrient concentrations do not exceed the
neutralising capacity and temperature do not
levels established so as to ensure the
show signs of anthropogenic disturbance and
functioning of the ecosystem and the
remain within the ranges normally associated
achievement of the values specified above for
with undisturbed conditions.
the biological quality elements.
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EN(3) in Section 1.2.2, the table ‘Physico-chemical quality elements’ is replaced by the following:
‘General physico-chemical quality elements
Element High status Good status Moderate status
General conditions The values of the general physico-chemical Temperature, oxygen balance, pH, acid Conditions consistent with the achievement of
elements correspond totally or nearly totally neutralising capacity, transparency and the values specified above for the biological
to undisturbed conditions. salinity do not reach levels outside the ranges quality elements.’;
established so as to ensure the functioning of
Nutrient concentrations remain within the
the ecosystem and the achievement of the
range normally associated with undisturbed
values specified above for the biological
conditions.
quality elements.
Levels of salinity, pH, oxygen balance, acid
Nutrient concentrations do not exceed the
neutralising capacity, transparency and
levels established so as to ensure the
temperature do not show signs of
functioning of the ecosystem and the
anthropogenic disturbance and remain
achievement of the values specified above for
within the ranges normally associated with
the biological quality elements.
undisturbed conditions.
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‘General physico-chemical quality elements
Element High status Good status Moderate status
General conditions The general physico-chemical elements Temperature, oxygenation conditions and Conditions consistent with the achievement of
correspond totally or nearly totally to transparency do not reach levels outside the the values specified above for the biological
undisturbed conditions. ranges established so as to ensure the quality elements.’;
functioning of the ecosystem and the
Nutrient concentrations remain within the
achievement of the values specified above for
range normally associated with undisturbed
the biological quality elements.
conditions.
Nutrient concentrations do not exceed the
Temperature, oxygen balance and
levels established so as to ensure the
transparency do not show signs of
functioning of the ecosystem and the
anthropogenic disturbance and remain
achievement of the values specified above for
within the ranges normally associated with
the biological quality elements.
undisturbed conditions.
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EN(5) in Section 1.2.4, the table ‘Physico-chemical quality elements’ is replaced by the following:
‘General physico-chemical quality elements
Element High status Good status Moderate status
General conditions The general physico-chemical elements Temperature, oxygenation conditions and Conditions consistent with the achievement of
correspond totally or nearly totally to transparency do not reach levels outside the the values specified above for the biological
undisturbed conditions. ranges established so as to ensure the quality elements.’;
functioning of the ecosystem and the
Nutrient concentrations remain within the
achievement of the values specified above for
range normally associated with undisturbed
the biological quality elements.
conditions.
Nutrient concentrations do not exceed the
Temperature, oxygen balance and
levels established so as to ensure the
transparency do not show signs of
functioning of the ecosystem and the
anthropogenic disturbance and remain
achievement of the values specified above for
within the ranges normally associated with
the biological quality elements.
undisturbed conditions.
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(6) in Section 1.2.5, the table is amended as follows:
(a) the fifth row for the entry ‘Specific synthetic pollutants’ is deleted;
(b) the sixth row for the entry ‘Specific non-synthetic pollutants’ is deleted;
(c) the seventh row for table note (1) is deleted;
(7) Section 1.2.6 is deleted;
(8) in Section 1.3, the following paragraphs are added:
‘Where the monitoring network involves earth observation and remote sensing rather than local sampling points, or
other innovative techniques, the map of the monitoring network shall include information on the quality elements
and the water bodies or groups of water bodies which have been monitored using such monitoring methods.
Reference shall be made to CEN, ISO, or other international or national standards that have been applied to ensure
that the temporal and spatial data obtained are as reliable as those obtained through the use of conventional
monitoring methods at local sampling and measuring points.
Member States may apply passive sampling methods to monitor chemical pollutants, where appropriate, in particular
for screening purposes and for long term assessment, on the condition that those sampling methods do not
underestimate the concentrations of pollutants for which environmental quality standards apply, and thus reliably
identify “failure to achieve good status”, and that chemical analysis of water, biota or sediment samples, according to
the environmental quality standards applied, is conducted wherever such failure is observed. Member States may also
apply effect-based monitoring methods subject to the same conditions.’;
(9) in Section 1.3.1, the last paragraph, ‘Selection of quality elements’, is replaced by the following:
‘Selection of quality elements
Surveillance monitoring shall be carried out for each monitoring site for a period of one year during the period
covered by a river basin management plan. The surveillance monitoring shall cover the following:
(a) parameters indicative of all biological quality elements;
(b) parameters indicative of all hydromorphological quality elements;
(c) parameters indicative of all general physico-chemical quality elements;
(d) priority substances which are discharged or otherwise deposited into the river basin or sub-basin;
(e) river basin specific pollutants.
However, where the previous surveillance monitoring exercise showed that the body concerned reached good status
and there is no evidence from the review of impact of human activity referred to in Annex II that the impacts on the
body have changed, the surveillance monitoring shall be carried out once during the period covered by three
consecutive river basin management plans.’;
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(10) Section 1.3.2 is amended as follows:
(a) in the third paragraph, ‘Selection of monitoring sites’, the introductory part is replaced by the following:
‘Operational monitoring shall be carried out for all those bodies of water which on the basis of either the impact
assessment carried out in accordance with Annex II or surveillance monitoring are identified as being at risk of
failing to meet their environmental objectives under Article 4 and for those bodies of water into which priority
substances are discharged or otherwise deposited or into which river basin specific pollutants are discharged or
otherwise deposited in significant quantities. Monitoring points shall be selected for priority substances as
specified in the legislation laying down the relevant environmental quality standard. In all other cases, including for
priority substances where no specific guidance is given in such legislation, monitoring points shall be selected as
follows:’;
(b) in the fourth paragraph, ‘Selection of quality elements’, the second indent is replaced by the following:
‘— all priority substances discharged or otherwise deposited into water bodies and all river basin specific
pollutants discharged or otherwise deposited into water bodies in significant quantities.’;
(11) in Section 1.3.4, the fourth paragraph is replaced by the following:
‘Monitoring frequencies shall be adjusted, if necessary, to take account of the variability in parameters resulting from
variation in both anthropogenic and natural conditions.
The times at which monitoring is undertaken shall be selected so as to take account of the impact of seasonal
variations in substance use or water levels on the monitoring results, and thus ensure that the results effectively reflect
any changes in the water body caused by anthropogenic pressure and by climatic variation. As regards priority
substances whose concentration is likely to peak over short periods as a result of seasonal fluctuations in their use,
monitoring shall, during those peak periods, be carried out at intervals shorter than for other substances, where
necessary, to ensure that adequate information is obtained on the concentration of those substances.’;
(12) in Section 1.3.4, in the table, the sixth row under the heading ‘Physico-chemical’, the words ‘Other pollutants’ are
replaced by ‘River basin specific pollutants’;
(13) Section 1.4.1 is amended as follows:
(a) in point (vii), the second sentence is deleted;
(b) point (viii) is deleted;
(c) point (ix) is replaced by the following:
‘(ix) The results of the intercalibration exercise and the values established for the Member State monitoring system
classifications in accordance with points (i) to (viii) shall be published within six months of the adoption of
the implementing act in accordance with Article 21.’;
(14) in Section 1.4.2 the following point is added:
‘(iv) Member States may provide additional maps that present the ecological quality information for one or more of
the following quality elements separately:
— Biological elements,
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— Hydromorphological elements supporting the biological elements,
— Physico-chemical elements supporting the biological elements.
Member States may also provide maps or tables indicating the degree of change for those quality elements
compared to the previous planning cycle.’;
(15) in Section 1.4.3, the first paragraph is replaced by the following:
‘A body of water shall be recorded as achieving good chemical status where it has a good surface water chemical status
as defined in Article 2(24). If not, the body shall be recorded as failing to achieve good chemical status.’;
(16) in Section 1.4.3, after the table with ‘Chemical status classification’ and ‘Colour code’ the following paragraphs are
inserted:
‘Member States may provide additional maps that present the chemical status information for one or more of the
following substances separately from the information for the rest of the substances identified in Part A of Annex I of
Directive 2008/105/EC:
(a) priority substances identified in Part A of Annex I of Directive 2008/105/EC as substances behaving like
ubiquitous persistent, bioaccumulative and toxic substances (uPBTs);
(b) newly identified priority substances in the latest review carried out by the Commission in accordance with
Article 16(2) of this Directive;
(c) priority substances for which revised and stricter EQS has been set in the latest review in accordance with
Article 16(2) of this Directive;
(d) substances identified as river basin specific pollutants according to Article 8d of Directive 2008/105/EC and based
on the assessment of pressures and impacts on surface water bodies carried out in accordance with Annex II to this
Directive.
Member States may also present the extent of any deviation from the EQS value for the substances referred to in points
(a) to (d) of the first subparagraph in the river basin management plans. Member States providing such additional
maps shall seek to ensure their inter-comparability at river basin and at Union level.’;
(17) in Section 2.2.1, the following paragraph is added:
‘Where the monitoring network involves earth observation methods or remote sensing rather than local sampling
points, or other innovative techniques, reference shall be made to CEN, ISO, or other international or national
standards that have been applied to ensure that the temporal and spatial data obtained are as reliable as those obtained
through the use of conventional monitoring methods at local sampling points.’;
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(18) Section 2.3.2 is replaced by the following:
‘2.3.2. Definition of good groundwater chemical status
Element Good status
Concentrations of pollutants The chemical composition of the groundwater body is such
that the concentrations of pollutants, as specified below:
— do not exhibit the effects of saline or other intrusions
— do not exceed the groundwater quality standards as
referred to in Annex I to Directive 2006/118/EC, the
threshold values for groundwater pollutants and
indicators of pollution set pursuant to Article 3 (1) (b), of
that Directive and the Union wide threshold values set
pursuant to Article 8 (3) of that Directive
— are not such as would result in failure to achieve the
environmental objectives specified under Article 4 for
associated surface waters nor any significant diminution
of the ecological or chemical quality of such bodies nor
in any significant damage to terrestrial ecosystems which
depend directly on the groundwater body
Conductivity Changes in conductivity are not indicative of saline or other
intrusion into the groundwater body’
(19) in Section 2.4.1, the following paragraph is added:
‘Where the monitoring network involves earth observation or remote sensing rather than local sampling points, or
other innovative techniques, reference shall be made to CEN, ISO, or other international or national standards that
have been applied to ensure that the temporal and spatial data obtained are as reliable as those obtained through the
use of conventional monitoring methods at local sampling points.’;
(20) in Section 2.4.3, under ‘operational monitoring’, the paragraph on ‘Frequency of monitoring’ is replaced by the
following:
‘Frequency of monitoring
Operational monitoring shall be carried out for the periods between surveillance monitoring programmes at
a frequency sufficient to detect the impacts of relevant pressures, including, where relevant, seasonal variation in the
use of substances and of short- and long-term variations in recharge that might affect chemical status parameters, and
at a minimum frequency of once per year, unless greater intervals would be justified on the basis of technical
knowledge and expert judgement, in particular if it can be shown that over successive years, no exceedance or
sustained upward trend has been detected for a particular parameter.’;
(21) Section 2.4.5 is replaced by the following:
‘2.4.5. Interpretation and presentation of groundwater chemical status
In assessing the chemical status of groundwater, the results of individual monitoring points within
a groundwater body shall be aggregated for the body as a whole. The mean value of the results of monitoring at
each point in the groundwater body or group of bodies shall be calculated for the following parameters:
(a) chemical parameters for which quality standards have been set in Annex I to Directive 2006/118/EC;
(b) chemical parameters for which national threshold values have been set pursuant to Article 3(1)(b) of
Directive 2006/118/EC;
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(c) chemical parameters for which Union wide threshold values have been set pursuant to Article 8(3) of
Directive 2006/118/EC.
The mean values referred to in the first paragraph shall be used to demonstrate compliance with good
groundwater chemical status defined by reference to the quality standards and threshold values referred to in
the first paragraph.
Subject to Section 2.5, Member States shall provide a map of groundwater chemical status, colour-coded as
follows:
Poor: red
Good: green
Member States may provide additional maps that present the chemical status information for one or more of
the following substances separately from the information for the rest of the substances identified in Directive
2006/118/EC:
(a) newly identified substances in the latest review in accordance with Article 8 of Directive 2006/118/EC;
(b) substances for which revised and stricter quality standards (QS) or threshold values are established in
accordance with Article 8 of Directive 2006/118/EC.
Member States may also present the extent of any deviation from the QS or threshold value for the substances
referred to in points (a) and (b) of the first subparagraph in the river basin management plans. Member States
providing such additional maps shall seek to ensure their inter-comparability at river basin and Union level.
Member States shall also indicate, by a black dot on the map, those groundwater bodies which are subject to
a significant and sustained upward trend in the concentrations of any pollutant resulting from the impact of
human activity. Reversal of such a trend shall be indicated by a blue dot on the map.
These maps shall be included in the river basin management plans.’.
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ANNEX II
Annex VIII to Directive 2000/60/EC is amended as follows:
(1) points 11 and 12 are deleted.
(2) the following point is added:
‘13. Microorganisms, genes or genetic material reflecting the presence of microorganisms resistant to antimicrobial
agents, in particular microorganisms pathogenic to humans or livestock.’.
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ANNEX III
Annex I to Directive 2006/118/EC is replaced by the following:
‘ANNEX I
QUALITY STANDARDS (QS) FOR GROUNDWATER POLLUTANTS AND INDICATORS OF POLLUTION
Where, for a given body of groundwater, it is considered that the groundwater quality standards could result in failure to
achieve the environmental objectives specified in Article 4 of Directive 2000/60/EC for associated bodies of surface water,
or in any significant deterioration of the ecological or chemical quality of such bodies, or in any significant damage to
terrestrial ecosystems which depend directly on that body of groundwater, more stringent threshold values shall be
established in accordance with Article 3 of and Annex II to this Directive. Provided that a reliable methodology is available
to assess the presence of groundwater ecosystems, more stringent quality standards shall also be established for
groundwater bodies where such ecosystems are present, unless the groundwater quality standards have been set to protect
human health and are already sufficiently strict to protect those ecosystems.
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Entry No Name of substance Category of substances CAS number(1) EU number(2) Quality Standard(3)[μg/l unless otherwise indicated]
1 Nitrates Nutrients not applicable not applicable 50 mg/l
2 Active substances in Pesticides not applicable not applicable 0,1 (individual)
pesticides, including their
relevant metabolites,
degradation and reaction
products(4)
0,5 (total)(5)
3 PFAS
3.1 Sum of PFAS Industrial substances See table note 6 See table note 6 The parametric value as defined in Part B of Annex I to Directive
(EU) 2020/2184(6)
3.2 Sum of 4 PFAS(7) Industrial substances See table note 7 See table note 7 0,0044(7)
4 Carbamazepine Pharmaceuticals 298-46-4 not applicable 2,5(12)
5 Sulfamethoxazole Pharmaceuticals 723-46-6 not applicable 0,1(12)
6 Primidone Pharmaceuticals 125-33-7 2,5(12)
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Entry No Name of substance Category of substances CAS number(1) EU number(2) Quality Standard(3)[μg/l unless otherwise indicated]
7 Non-relevant metabolites of Pesticides not applicable not applicable 1 or up to 5(8) (individual)
pesticides (nrMs)(4)
5(9) or 12,5(10) (total)(11)
8 Trichloroethylene and Industrial substances 79-01-6 and 201-167-4 and 10 (total)(13)
Tetrachloroethylene (sum 127-18-4 204-825-9
of two)
(1) CAS: Chemical Abstracts Service.
(2) EU number: European Inventory of Existing Commercial Substances (EINECS) or European List of Notified Chemical Substances (ELINCS).
(3) This parameter is the QS expressed as an annual average value. Unless otherwise specified, it applies to the total concentration of all substances and isomers.
(4) “Pesticides” means plant protection products and biocidal products referred to in Article 2 of Regulation (EC) No 1107/2009 and in Article 3 of Regulation (EU) No 528/2012 respectively.
For that parameter, Member States shall monitor the active substances present in pesticidal products currently or previously used in their territory and any found to be present as a result of transboundary
pollution, and their relevant and non-relevant metabolites, degradation and reaction products, drawing, when available, on the list to be established in accordance with Article 4(2a) of this Directive. Member States
may stop monitoring specific active substances and their metabolites if they are no longer being used in their territory, provided that past monitoring has consistently shown that those substances and metabolites
do not occur in the groundwater body.
A pesticide metabolite shall be deemed relevant if there is reason to consider that it has intrinsic properties comparable to those of the parent active substance in terms of its toxicity for the target pest or that either
itself or its transformation products generate a health risk for consumers or the environment.
(5) “Total” means the sum of all individual pesticides detected and quantified in the monitoring procedure, including their relevant metabolites, degradation and reaction products.
(6) This refers to the PFAS listed in point 3 of Part B of Annex III to Directive (EU) 2020/2184. The parameter and the quality standard shall be updated according to amendments to that Directive.
(7) This refers to the following compounds, listed with their CAS number and EU number: Perfluorohexane sulfonic acid (PFHxS), (CAS 355-46-4, EU 206-587-1); Perfluorooctanesulfonic acid (PFOS) (CAS
1763-23-1, EU 217-179-8); Perfluorooctanoic acid (PFOA) (CAS 335-67-1, EU 206-397-9); Perfluorononanoic acid (PFNA) (CAS 375-95-1, EU 206-801-3). For the sum of 4 PFAS, the CAS numbers listed refer
only to the protonated form of the individual PFAS but the sum applies to the total concentration of the dissolved substances including protonated and deprotonated forms and their isomers linear and branched.
(8) Member States shall apply a default quality standard of 1 μg/l unless they provide reliable evidence, including from tests of acute and chronic toxicity on the taxonomic group confidently predicted to be the most
sensitive, that a more or less strict standard is justified, in which case they shall apply that standard, up to a maximum of 5 μg/l.
(9) The total concentration of nrMs for which the default quality standard of 1 μg/l for individual nrMs applies, or a stricter standard, shall not exceed 5 μg/l.
(10) The total concentration of nrMs for which standards above 1 and up to 5 μg/l for individual nrMs apply shall not exceed 12,5 μg/l.
(11) “Total” means the sum of all individual nrMs in each individual quality-standard category detected and quantified in the monitoring procedure, which should cover at least the nrMs listed in accordance with
Article 4(2a).
(12) When a reliable methodology is available, Member States shall assess the presence of groundwater ecosystems in groundwater bodies whose characteristics could support their existence and set, if such ecosystems
are present, and in line with Article 3(1)(b), a stricter threshold value for this substance that is adequate to protect those ecosystems.
(13) “Total” means the sum of concentrations of Trichloroethylene and Tetrachloroethylene.’.
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ANNEX IV
Annex II of Directive 2006/118/EC is amended as follows:
(1) in Part A, the following paragraph is inserted after the first paragraph:
‘In accordance with Article 15 of Directive 2000/60/EC, Member States shall ensure that competent authorities
inform the Commission of threshold values for pollutants and indicators of pollution.’;
(2) in Part B, point 2 is replaced by the following:
‘2. Man-made synthetic substances(*)
Trichloroethylene
Tetrachloroethylene
(*) including synthetic substances with identical natural counterparts which may occur in groundwater, but where
any natural background level is, at most, low.’;
(3) in Part C, the title is replaced by the following:
‘Information to be provided by Member States with regard to the pollutants and indicators of pollution for which
threshold values have been established by the Member States’;
(4) the following Part is added:
‘Part D
Repository of harmonised threshold values for man-made synthetic substances(*) in groundwater of national,
regional or local concern
(*) including synthetic substances with identical natural counterparts which may occur in groundwater, but where any natural
background level is, at most, low.
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Threshold value
Entry No Name of substance Category of substances CAS number(1) EU number(2)
[μg/l unless otherwise indicated]
Individual pharmaceutical active Pharmaceuticals 2,5(4)
substances(3)
(1) CAS: Chemical Abstracts Service.
(2) EU number: European Inventory of Existing Commercial Substances (EINECS) or European List of Notified Chemical Substances (ELINCS).
(3) Pharmaceutical active substances as defined in Directive 2001/83/EC and Regulation (EU) 2019/6.
(4) Member States shall apply this threshold value unless a standard or threshold value has been specifically set for the substance concerned at Union or national level for either surface or groundwater. When a reliable
methodology is available, Member States shall assess the presence of groundwater ecosystems in groundwater bodies whose characteristics could support their existence and set, if such ecosystems are present, and
in accordance with Article 3(1)(b), a stricter threshold value if necessary to protect those ecosystems.’.
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ENANNEX V
The following Annex is added in Directive 2006/118/EC
‘ANNEX V
SUBSTANCES SUBJECT TO REVIEW FOR POSSIBLE INCLUSION IN ANNEX I WITH A UNION-WIDE GROUNDWATER QUALITY STANDARD
(1) (2) (3) (4) (5) (6)
Threshold value
Entry No Name of substance Category of substances CAS number(1) EU number(2)
[μg/l unless otherwise indicated]
Sum(s) of selected pharmaceuticals by Pharmaceuticals
mode of action
Sum of bisphenols Industrial substances
(1) CAS: Chemical Abstracts Service.
(2) EU number: European Inventory of Existing Commercial Substances (EINECS) or European List of Notified Chemical Substances (ELINCS).’.
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ANNEX VI
Annex I to Directive 2008/105/EC is amended as follows:
(1) the title is replaced by the following:
‘ENVIRONMENTAL QUALITY STANDARDS (EQS) FOR PRIORITY SUBSTANCES IN SURFACE WATERS’;
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‘PART A: ENVIRONMENTAL QUALITY STANDARDS
(1) (2) (3) (4) (5) (6) (7) (8) (9) (10) (11) (12) (13)
EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(1) The substance Alachlor has been moved to Part C of Annex II
(2) Anthracene Industrial 120-12-7 204-371-1 0,1 0,1 0,1 0,1 X X
substances
(3) The substance Atrazine has been moved to Part C of Annex II
(4) Benzene Industrial 71-43-2 200-753-7 10 8 50 50
substances
(5) Brominated Industrial not applicable not applicable 0,14 0,014(7) 0,00028(7) X(8) X X
diphenylethers(7) substances
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(6) Cadmium and its Metals 7440-43-9 231-152-8 ≤ 0,08 0,2 ≤ 0,45 ≤ 0,45 X X
compounds (Class 1) (Class 1) (Class 1)
(depending on water 0,08 (Class 2) 0,45 (Class 2) 0,45 (Class 2)
hardness classes)(9)
0,09 (Class 3) 0,6 (Class 3) 0,6 (Class 3)
0,15 (Class 4) 0,9 (Class 4) 0,9 (Class 4)
0,25 (Class 5) 1,5 (Class 5) 1,5 (Class 5)
(6a) The substance Carbon tetrachloride has been moved to Part C of Annex II
(7) C Chloroalkanes(10) Industrial 85535-84-8 287-476-5 0,4 0,4 1,4 1,4 X X
10-13
substances
(8) The substance Chlorfenvinphos has been moved to Part C of Annex II
(9) Chlorpyrifos Pesticides – 2921-88-2 220-864-4 4,6 × 10-4 4,6 × 10-5 0,0026 5,2 × 10-4 X X X
(Chlorpyrifos-ethyl) organophosphate
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EN(1) (2) (3) (4) (5) (6) (7) (8) (9) (10) (11) (12) (13)
EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(9a) Cyclodiene pesticides: Pesticides – 309-00-2 206-215-8 Σ = 0,01 Σ = 0,005 not applicable not applicable X
organochlorine
Aldrin 60-57-1 200-484-5
Dieldrin 72-20-8 200-775-7
Endrin 465-73-6 207-366-2
Isodrin
(9b) DDT total(11) Pesticides – not applicable not applicable 0,025 0,025 not applicable not applicable X
organochlorine
para-para-DDT 50-29-3 200-024-3 0,01 0,01 not applicable not applicable X
(10) 1,2-Dichloroethane Industrial 107-06-2 203-458-1 10 10 not applicable not applicable X
substances
(11) Dichloromethane Industrial 75-09-2 200-838-9 20 20 not applicable not applicable
substances
(12) Di(2-ethylhexyl)-phthalate Industrial 117-81-7 204-211-0 1,3 1,3 not applicable not applicable X X
(DEHP) substances
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Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(13) Diuron Pesticides – 330-54-1 206-354-4 0,049 0,0049 0,27 0,054
herbicide
(14) Endosulfan Pesticides – 115-29-7 204-079-4 0,005 0,0005 0,01 0,004 X
organochlorine
(15) Fluoranthene Industrial 206-44-0 205-912-4 7,62 × 10-4 7,62 × 10-4 0,12 0,012 6,1 X X X
substances
(16) Hexachlorobenzene Pesticides – 118-74-1 204-273-9 0,5 0,05 8 fw fish X X
organochlorine
1 sw fish
(17) Hexachlorobutadiene Industrial 87-68-3 201-765-5 9,5 x 10-4 9,5 × 10-4 0,6 0,06 21 X X
substances
(solvents)
(18) Hexachlorocyclohexane Pesticides – 608-73-1 210-168-9 0,02 0,002 0,04 0,02 X X
insecticides
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(19) Isoproturon Pesticides – 34123-59-6 251-835-4 0,3 0,3 1,0 1,0
herbicide
(20) Lead and its compounds Metals 7439-92-1 231-100-4 1,2(12) 1,3 14 14 X X
(21) Mercury and its Metals 7439-97-6 231-106-7 0,07 0,07 11 X X X
compounds
(22) Naphthalene Industrial 91-20-3 202-049-5 2 2 130 130
substances
(23) Nickel and its compounds Metals 7440-02-0 231-111-4 2(12) 3,1 8,2 8,2
(24) Nonylphenols(13) Industrial see footnote see footnote 0,037 0,0018 2,1 0,17 X
(4-Nonylphenol) substances 13 13
(25) Octylphenols(14)((4- Industrial see footnote see footnote 0,1 0,01 not applicable not applicable X
(1,1’,3,3’- substances 14 14
tetramethylbutyl)-phenol))
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(26) Pentachlorobenzene Industrial 608-93-5 210-172-0 0,007 0,0007 not applicable not applicable X X
substances
(27) Pentachlorophenol Pesticides – 87-86-5 201-778-6 0,4 0,4 1 1 X
organochlorine
(28) Polyaromatic Combustion not applicable not applicable not applicable not applicable not applicable not applicable Sum of Benzo X X X
hydrocarbons (PAHs)(15) products (a)pyrene
equivalents
0,6(16)
Benzo(a)pyrene 50-32-8 200-028-5 0,5 0,05 0,6
Benzo(b)fluoranthene 205-99-2 205-911-9 0,017 0,017 see footnote
16
Benzo(k)fluoranthene 207-08-9 205-916-6 0,017 0,017 see footnote
16
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
Benzo(g,h,i)perylene 191-24-2 205-883-8 8,2 × 10-3 8,2 × 10-4 see footnote
16
Indeno(1,2,3-cd)pyrene 193-39-5 205-893-2 not applicable not applicable see footnote
16
Chrysene 218-01-9 205-923-4 0,07 0,007 see footnote
16
Benzo(a)anthracene 56-55-3 200-280-6 0,1 0,01 see footnote
16
Dibenz(a,h)anthracene 53-70-3 200-181-8 0,014 0,0014 see footnote
16
Fluoranthene 206-44-0 205-912-4 0,12 0,012 see footnote
16
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(29) The substance Simazine has been moved to Part C of Annex II
(29a) Tetrachloroethylene Industrial 127-18-4 204-825-9 10 10 not applicable not applicable
substances
(29b) Trichloroethylene Industrial 79-01-6 201-167-4 10 10 not applicable not applicable X
substances
(30) Tributyltin compounds(17) Pesticides – biocide 36643-28-4 not applicable 0,0002 0,0002 0,0015 0,0015 1,6(18) X X X
(Tributyltin-cation)
(31) The substance Trichlorobenzenes has been moved to Part C of Annex II
(32) Trichloromethane Industrial 67-66-3 200-663-8 2,5 2,5 not applicable not applicable
substances
(33) Trifluralin Pesticides – 1582-09-8 216-428-8 0,03 0,03 not applicable not applicable X
herbicides
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(34) Dicofol Pesticides – 115-32-2 204-082-0 4,45 × 10-3 0,185 × 10-3 not not 111 fw fish X X
organochlorine applicable(19) applicable(19)
4,6 sw fish
(35) Perfluorooctane sulfonic Industrial 1763-23-1 217-179-8 Covered by substance group 65 (Per- and polyfluoroalkyl substances (PFAS) – sum of 25)
acid (PFOS) and its substances
derivatives
(36) Quinoxyfen Pesticides – 124495-18-7 not applicable 0,15 0,015 2,7 0,54 X X
fungicide
(37) Dioxins and dioxin-like Industrial not applicable not applicable not applicable not applicable Sum of X X X
compounds(20) byproducts PCDDs+
PCDFs+
PCB-DLs
equivalents
3,5 × 10-5(21)
(38) Aclonifen Pesticides – 74070-46-5 277-704-1 0,12 0,012 0,12 0,012
herbicide
(39) Bifenox Pesticides – 42576-02-3 255-894-7 0,012 0,0012 0,04 0,004
herbicide
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(40) Cybutryne Pesticides – biocide 28159-98-0 248-872-3 0,0025 0,0025 0,016 0,016
(41) Cypermethrin(22) Pesticides – 52315-07-8 257-842-9 3 × 10-5 3 × 10-6 6 × 10-4 6 × 10-5 X
pyrethroid
(42) Dichlorvos Pesticides – 62-73-7 200-547-7 6 × 10-4 6 × 10-5 7 × 10-4 7 × 10-5
organophosphate
(43) Hexabromocyclododecane Industrial See footnote See footnote 4,6 × 10-4 2 × 10-5 0,5 0,05 90 fw fish X X X
(HBCDD)(23) substances 23 23
3,5 sw fish
(44) Heptachlor and heptachlor Pesticides – 76-44-8 / 200-962-3/ 1,7 × 10-7 1,7 × 10-7 3 × 10-4 3 × 10-5 0,013 X X X
epoxide organochlorine 1024-57-3 213-831-0
(45) Terbutryn Pesticides – biocides 886-50-0 212-950-5 0,065 0,0065 0,34 0,034
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(46) 17 alpha-ethinylestradiol Pharmaceuticals – 57-63-6 200-342-2 1,7 × 10-5 1,6 × 10-6 not derived not derived
(EE2) estrogenic hormone
(47) 17 beta-estradiol (E2) Pharmaceuticals – 50-28-2 200-023-8 0,00018 9 × 10-6 not derived not derived
estrogenic hormone
(48) Acetamiprid Pesticides – 135410-20-7 / 603-921-1 0,037 0,0037 0,16 0,016
neonicotinoid 160430-64-8
(49) Azithromycin Pharmaceuticals – 83905-01-5 617-500-5 0,019 0,0019 0,18 0,018 X
macrolide antibiotic
(50) Bifenthrin Pesticides – 82657-04-3 617-373-6 9,5 × 10-5 9,5 × 10-6 0,011 0,001 X
pyrethroid
(51) Bisphenol-A (BPA) Industrial 80-05-7 201-245-8 1,7 x 10-4 1,7 x 10-4 130 51 0,025 X
substances
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Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(52) Carbamazepine Pharmaceuticals – 298-46-4 206-062-7 2,5 0,25 1,6 × 103 160
anticonvulsant
(53) Clarithromycin Pharmaceuticals – 81103-11-9 658-034-2 0,13 0,013 0,13 0,013 X
macrolide antibiotic
(54) Clothianidin Pesticides 210880-92-5 433-460-1 0,01 0,001 0,34 0,034
-neonicotinoid
(55) Deltamethrin Pesticides – 52918-63-5 258-256-6 1,7 × 10-6 1,7 × 10-7 1,7 × 10-5 3,4 × 10-6 X
pyrethroid
(56) Diclofenac Pharmaceuticals – 15307-86-5 / 239-348-5 / 0,04 0,004 250 25 X
anti-inflammatory 15307-79-6 239-346-4
(57) Erythromycin Pharmaceuticals – 114-07-8 204-040-1 0,5 0,05 1 0,1 X
macrolide antibiotic
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(58) Esfenvalerate Pesticides – 66230-04-4 613-911-9 1,7 × 10-5 1,7 × 10-6 0,0085 0,00085 X
pyrethroid
(59) Estrone (E1) Pharmaceuticals – 53-16-7 200-164-5 3,6 × 10-4 1,8 × 10-5 not derived not derived
estrogenic hormone
(60) Glyphosate Pesticides – 1071-83-6 213-997-4 0,1(24) 8,67 not 39,86
herbicide applicable(24)
86,7(25)
398,6(25)
(61) Ibuprofen Pharmaceuticals – 15687-27-1 239-784-6 0,14 0,014 X
anti-inflammatory
(62) Imidacloprid Pesticides – 138261-41-3 / 428-040-8 0,0068 6,8 × 10-4 0,057 0,0057
neonicotinoid 105827-78-9
(63) Nicosulfuron Pesticides – 111991-09-4 601-148-4 0,0087 8,7 × 10-4 0,23 0,023
herbicide
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(64) Permethrin Pesticides – 52645-53-1 258-067-9 2,7 × 10-4 2,7 × 10-5 0,0025 2,5 × 10-4 X
pyrethroid
(65) Per- and polyfluoroalkyl Industrial not applicable not applicable Sum of PFOA Sum of PFOA not applicable not applicable Sum of PFOA X X X
substances (PFAS) – sum of substances equivalents equivalents equivalents
25(26)(29) 0,0044(27) 0,0044(27) 0,077(27)
(66) Silver Metals 7440-22-4 231-131-3 0,01 0,006 (10‰ 0,022 not derived
salinity)
0,17 (30‰
salinity)
(67) Thiacloprid Pesticides – 111988-49-9 601-147-9 0,01 0,001 0,05 0,005
neonicotinoid
(68) Thiamethoxam Pesticides – 153719-23-4 428-650-4 0,04 0,004 0,77 0,077
neonicotinoid
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(69) Triclosan Pesticides – biocides 3380-34-5 222-182-2 0,02 0,002 0,02 0,002
(70) Sum of active substances Pesticides not applicable not applicable 0,2(30)
in the pesticides(28)listed
in this table(29)(30)
(1) CAS: Chemical Abstracts Service.
(2) EU number: European Inventory of Existing Commercial Substances (EINECS) or European List of Notified Chemical Substances (ELINCS).
(3) This parameter is the EQS expressed as an annual average value (AA-EQS). Unless otherwise specified, it applies to the total concentration of all substances and isomers.
(4) Inland surface waters encompass rivers and lakes and related artificial or heavily modified water bodies.
(5) This parameter is the EQS expressed as a maximum allowable concentration (MAC EQS). Unless otherwise specified, it applies to the total concentration of all substances and isomers. Where the MAC EQS are marked as “not applicable”,
the AA EQS values are considered protective against short-term pollution peaks in continuous discharges since they are significantly lower than the values derived on the basis of acute toxicity.
(6) If an EQS for biota or sediment is given, it, rather than the water EQS, shall be applied, without prejudice to Article 3(3) of this Directive allowing an alternative biota taxon, or another matrix, to be monitored instead, as long as the EQS
applied provides an equivalent level of protection. Unless otherwise specified, it applies to the total concentration of all substances and isomers. Unless otherwise indicated, the biota EQS relate to fish. “fw fish” indicates the biota EQS for
freshwater fish monitored in inland waters; “sw fish” indicates the biota EQS for saltwater fish monitored in other surface waters. For substances numbered 15 (Fluoranthene), 28 (PAHs), and 51 (Bisphenol-A) the biota EQS refers to
crustaceans and molluscs. For the purpose of assessing chemical status, monitoring of Fluoranthene PAHs, and Bisphenol-A in fish is not appropriate. For substance number 37 (Dioxins and dioxin-like compounds), the biota EQS relates to
fish, crustaceans and molluscs, in line with point 4.1.5 of Annex I to Commission Regulation (EU) 2023/915 (*).
(7) For the group of priority substances covered by brominated diphenylethers (No 5), the EQS refer to the sum of the concentrations of congener numbers 28, 47, 99, 100, 153 and 154.
(8) Tetra, Penta, Hexa, Hepta, Octa and Decabromodiphenylether (CAS numbers 40088-47-9, 32534-81-9, 36483-60-0, 68928-80-3, 32536-52-0, 1163-19-5, respectively).
(9) For Cadmium and its compounds (No 6) the EQS values vary depending on the hardness of the water as specified in five class categories (Class 1: < 40 mg CaCO/l, Class 2: 40 to < 50 mg CaCO/l, Class 3: 50 to < 100 mg CaCO/l, Class 4:
3 3 3 100 to < 200 mg CaCO/l and Class 5: ≥ 200 mg CaCO/l).
3 3 (10) No indicative parameter is provided for this group of substances. The indicative parameter(s) shall be defined through the analytical method.
(11) DDT total comprises the sum of the isomers 1,1,1 trichloro 2,2 bis (p chlorophenyl) ethane (CAS 50 29 3, EU 200 024 3); 1,1,1 trichloro 2 (o chlorophenyl) 2 (p chlorophenyl) ethane (CAS 789 02 6, EU 212 332 5); 1,1-dichloro 2,2 bis
(p chlorophenyl) ethylene (CAS 72 55 9, EU 200 784 6); and 1,1 dichloro 2,2 bis (p chlorophenyl) ethane (CAS 72 54 8, EU 200 783 0).
(12) These EQS refer to bioavailable concentrations of the substances.
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EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(13) Nonylphenol (CAS 25154-52-3, EU 246-672-0) including isomers 4-nonylphenol (CAS 104-40-5, EU 203-199-4) and 4-nonylphenol (branched) (CAS 84852-15-3, EU 284-325-5).
(14) Octylphenol (CAS 1806-26-4, EU 217-302-5) including isomer 4-(1,1’,3,3’-tetramethylbutyl)-phenol (CAS 140-66-9, EU 205-426-2).
(15) Benzo(a)pyrene (CAS 50-32-8) (RPF 1), benzo(b)fluoranthene (CAS 205-99-2) (RPF 0,1), benzo(k)fluoranthene (CAS 207-08-9) (RPF 0,1), benzo(g,h,i)perylene (CAS 191-24-2) (RPF 0), indeno(1,2,3-cd)pyrene (CAS 193-39-5) (RPF 0,1),
chrysene (CAS 218-01-9) (RPF 0,01), benzo(a)anthracene (CAS 56-55-3) (RPF 0,1), dibenz(a,h)anthracene (CAS 53-70-3) (RPF 1) and fluoranthene (CAS 206-44-0) (RPF 0,01). Fluoranthene also appears separately in row 15. The PAHs
anthracene and naphthalene are listed only separately because no RPF is available.
(16) For the group of polyaromatic hydrocarbons (PAHs) (No 28), the biota EQS refers to the sum of the concentrations of eight of the nine PAHs listed in footnote 15 expressed as benzo(a)pyrene equivalents based on the carcinogenic
potencies of the substances relative to that of benzo(a)pyrene, i.e. the RPFs in footnote 15. Benzo(g,h,i)perylene does not need to be measured in biota for the purposes of determining compliance with the overall biota EQS. The biota EQS
for fluoranthene in row 15 must also be complied with.
(17) Tributyltin compounds including tributyltin-cation (CAS 36643-28-4).
(18) Sediment EQS.
(19) There is insufficient information available to set a MAC-EQS for these substances.
(20) This refers to the following compounds:
7 polychlorinated dibenzo-p-dioxins (PCDDs): 2,3,7,8-T4CDD (CAS 1746-01-6, EU 217-122-7), 1,2,3,7,8-P5CDD (CAS 40321-76-4), 1,2,3,4,7,8-H6CDD (CAS 39227-28-6), 1,2,3,6,7,8-H6CDD (CAS 57653-85-7), 1,2,3,7,8,9-H6CDD
(CAS 19408-74-3), 1,2,3,4,6,7,8-H7CDD (CAS 35822-46-9), 1,2,3,4,6,7,8,9-O8CDD (CAS 3268-87-9)
10 polychlorinated dibenzofurans (PCDFs): 2,3,7,8-T4CDF (CAS 51207-31-9), 1,2,3,7,8-P5CDF (CAS 57117-41-6), 2,3,4,7,8-P5CDF (CAS 57117-31-4), 1,2,3,4,7,8-H6CDF (CAS 70648-26-9), 1,2,3,6,7,8-H6CDF (CAS 57117-44-9),
1,2,3,7,8,9-H6CDF (CAS 72918-21-9), 2,3,4,6,7,8-H6CDF (CAS 60851-34-5), 1,2,3,4,6,7,8-H7CDF (CAS 67562-39-4), 1,2,3,4,7,8,9-H7CDF (CAS 55673-89-7), 1,2,3,4,6,7,8,9-O8CDF (CAS 39001-02-0)
12 dioxin-like polychlorinated biphenyls (PCB-DLs): 3,3’,4,4’-T4CB (PCB 77, CAS 32598-13-3), 3,3’,4’,5-T4CB (PCB 81, CAS 70362-50-4), 2,3,3’,4,4’-P5CB (PCB 105, CAS 32598-14-4), 2,3,4,4’,5-P5CB (PCB 114, CAS 74472-37-0),
2,3’,4,4’,5-P5CB (PCB 118, CAS 31508-00-6), 2,3’,4,4’,5’-P5CB (PCB 123, CAS 65510-44-3), 3,3’,4,4’,5-P5CB (PCB 126, CAS 57465-28-8), 2,3,3’,4,4’,5-H6CB (PCB 156, CAS 38380-08-4), 2,3,3’,4,4’,5’-H6CB (PCB 157, CAS
69782-90-7), 2,3’,4,4’,5,5’-H6CB (PCB 167, CAS 52663-72-6), 3,3’,4,4’,5,5’-H6CB (PCB 169, CAS 32774-16-6), 2,3,3’,4,4’,5,5’-H7CB (PCB 189, CAS 39635-31-9).
(21) For the group of Dioxins and dioxin-like compounds (No 37), the biota EQS refers to the sum of the concentrations of the substances listed in footnote 20 expressed as toxic equivalents based on the World Health Organisation 2005 Toxic
Equivalence Factors.
(22) CAS 52315-07-8 refers to an isomer mixture of cypermethrin, alpha-cypermethrin (CAS 67375-30-8, EU 257-842-9), beta-cypermethrin (CAS 65731-84-2, EU 265-898-0), theta-cypermethrin (CAS 71691-59-1) and zeta-cypermethrin
(CAS 1315501-18-8, EU 257-842-9).
(23) This refers to 1,3,5,7,9,11-Hexabromocyclododecane (CAS 25637-99-4, EU 247-148-4), 1,2,5,6,9,10-Hexabromocyclododecane (CAS 3194-55-6, EU 221-695-9), α-Hexabromocyclododecane (CAS 134237-50-6),
β-Hexabromocyclododecane (CAS 134237-51-7) and γ-Hexabromocyclododecane (CAS 134237-52-8).
(24) For freshwater used for the abstraction and preparation of drinking water.
(25) For freshwater not used for the abstraction and preparation of drinking water.
(26) This refers to the following compounds, listed with their CAS number, EU number and Relative Potency Factor (RPF):
Perfluorooctanoic acid (PFOA) (CAS 335-67-1, EU 206-397-9) (RPF 1), Perfluorooctane sulfonic acid (PFOS) (CAS 1763-23-1, EU 217-179-8) (RPF 2), Perfluorohexane sulfonic acid (PFHxS) (CAS 355-46-4, EU 206-587-1) (RPF 0,6),
Perfluorononanoic acid (PFNA) (CAS 375-95-1, EU 206-801-3) (RPF 10), Perfluorobutane sulfonic acid (PFBS) (CAS 375-73-5, EU 206-793-1) (RPF 0,001), Perfluorohexanoic acid (PFHxA) (CAS 307-24-4, EU 206-196-6) (RPF 0,01),
Perfluorobutanoic acid (PFBA) (CAS 375-22-4, EU 206-786-3) (RPF 0,05), Perfluoropentanoic acid (PFPeA) (CAS 2706-90-3, EU 220-300-7) (RPF 0,03), Perfluoropentane sulfonic acid (PFPeS) (CAS 2706-91-4, EU 220-301-2) (RPF
0,3005), Perfluorodecanoic acid (PFDA) (CAS 335-76-2, EU 206-400-3) (RPF 7), Perfluorododecanoic acid (PFDoDA or PFDoA) (CAS 307-55-1, EU 206-203-2) (RPF 3), Perfluoroundecanoic acid (PFUnDA or PFUnA) (CAS 2058-94-8, EU
218-165-4) (RPF 4), Perfluoroheptanoic acid (PFHpA) (CAS 375-85-9, EU 206-798-9) (RPF 0,505), Perfluorotridecanoic acid (PFTrDA) (CAS 72629-94-8, EU 276-745-2) (RPF 1,65), Perfluoroheptane sulfonic acid (PFHpS) (CAS
375-92-8, EU 206-800-8) (RPF 1,3), Perfluorodecane sulfonic acid (PFDS) (CAS 335-77-3, EU 206-401-9) (RPF 2), Perfluorotetradecanoic acid (PFTeDA) (CAS 376-06-7, EU 206-803-4) (RPF 0,3), Perfluorohexadecanoic acid (PFHxDA)
(CAS 67905-19-5, EU 267-638-1) (RPF 0,02), Perfluorooctadecanoic acid (PFODA) (CAS 16517-11-6, EU 240-582-5) (RPF 0,02), 2,3,3,3-tetrafluoro-2-(heptafluoropropoxy)propionic acid (HFPO-DA) (CAS 13252-13-6) (RPF 0,06),
2,2,3-trifluoro-3-(1,1,2,2,3,3-hexafluoro-3-(trifluoromethoxy)propoxy)propanoic acid (CAS 919005-14-4) (RPF 0,03), 2- (Perfluorohexyl)ethyl alcohol (6:2 FTOH) (CAS 647-42-7, EU 211-477-1) (RPF 0,02), 2-(Perfluorooctyl)ethanol
(8:2 FTOH) (CAS 678-39-7, EU 211-648-0) (RPF 0,04) and 2,2-difluoro-2-((2,2,4,5-tetrafluoro-5-(trifluoromethoxy)-1,3-dioxolan-4-yl)oxy) acetic acid (C6O4) (CAS 1190931-41-9) (RPF 0,06), Trifluoroacetic acid (TFA) (CAS 76-05-1,
EU 200-929-3) (RPF 0,002).
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EN(1) (2) (3) (4) (5) (6) (7) (8) (9) (10) (11) (12) (13)
EQS Identified as
Biota(6) an
Identified as
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) [μg/kg wet Identified Ubiquitous a substance
weight] as Persistent,
Entry Inland surface Other surface Inland surface Other surface that tends to
No Name of substance Category of substances CAS number(1) EU number(2) waters(4) waters waters(4) waters or EQS a priority Bioaccu- accumulate in
[μg/l] [μg/l] [μg/l] [μg/l] Sediment hazardous - sediment
[μg /kg dry substance mulative and and/or biota
weight] where Toxic (uPBT)
so indicated substance
(27) For the group of PFAS (No 65), the EQS refer to the sum of the concentrations of the 25 PFAS listed in footnote 26 expressed as PFOA-equivalents based on the potencies of the substances relative to that of PFOA, i.e. the RPFs in footnote
26. The critical EQS is the biota EQS (relating to fish consumption) and must therefore be complied with. The AA-EQS are not equivalently protective.
(28) “Pesticides” means plant protection products as referred to in Article 2 of Regulation (EC) No 1107/2009 and biocidal products as defined in Article 3 of Regulation (EU) No 528/2012.
(29) The minimum performance criteria laid down in Directive 2009/90/EC apply to each individual substance within the group of substances but taking account of the need to quantify the contribution of each substance to the total
concentration for comparison with the EQS.
(30) With the following exceptions: the four pesticides to be monitored in biota or sediment, i.e. the substances numbered 16, 30, 34 and 44, and glyphosate.
(*) Commission Regulation (EU) 2023/915 of 25 April 2023 on maximum levels for certain contaminants in food and repealing Regulation (EC) No 1881/2006 (OJ L 119, 5.5.2023, p. 103, ELI: http://data.europa.eu/eli/reg/2023/915/oj).’;
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(3) Part B is amended as follows:
(a) in point 1, the first paragraph is replaced by the following:
‘For any given surface water body, applying the AA-EQS means that, for each representative monitoring point
within the water body, the arithmetic mean of the concentrations measured at different times during the year does
not exceed the standard.’;
(b) in point 2, the first paragraph is replaced by the following:
‘For any given surface water body, applying the MAC-EQS means that the measured concentration at any
representative monitoring point within the water body does not exceed the standard.’.
ELI: http://data.europa.eu/eli/dir/2026/805/oj 81/84EN
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ANNEX VII
The following Annex is added to Directive 2008/105/EC:
‘ANNEX II
ENVIRONMENTAL QUALITY STANDARDS FOR RIVER BASIN SPECIFIC POLLUTANTS
PART A: INDICATIVE LIST OF CATEGORIES OF RIVER BASIN SPECIFIC POLLUTANTS
1. Organohalogen compounds and substances which may form such compounds in the aquatic environment.
2. Organophosphorous compounds.
3. Organotin compounds.
4. Substances and preparations, or the breakdown products of such, which have been proved to possess carcinogenic or
mutagenic properties or properties which may affect steroidogenic, thyroid, reproduction or other endocrine-related
functions in or via the aquatic environment.
5. Persistent hydrocarbons and persistent and bioaccumulable organic toxic substances.
6. Cyanides.
7. Metals and their compounds.
8. Arsenic and its compounds.
9. Biocides and plant protection products.
10. Materials in suspension, including micro/nanoplastics
11. Microorganisms, genes or genetic material reflecting the presence of microorganisms resistant to antimicrobial agents,
in particular microorganisms pathogenic to humans or livestock.
PART B: THE PROCEDURE FOR DERIVING ENVIRONMENTAL QUALITY STANDARDS FOR RIVER BASIN SPECIFIC POLLUTANTS
Methods used for the establishment of EQS for river basin specific pollutants shall include the following steps:
(a) identification of the receptors and compartments or matrices at risk from the substance of concern;
(b) collation and quality assessment of data on the properties of the substance of concern, including its (eco)toxicity, in
particular from reports on laboratory, mesocosm and field studies which cover both chronic and acute effects in both
fresh and saltwater environments;
(c) extrapolation of (eco)toxicity data to no-effect or similar concentrations using deterministic or probabilistic methods,
and selection and application of appropriate assessment factors to address uncertainties and derive EQS;
(d) comparison of EQS for different receptors and compartments, and selection of critical EQS, i.e. the EQS that provides
protection to the most sensitive receptor in the most relevant compartment or matrix.
82/84 ELI: http://data.europa.eu/eli/dir/2026/805/ojPART C: REPOSITORY OF HARMONISED ENVIRONMENTAL QUALITY STANDARDS FOR RIVER BASIN SPECIFIC POLLUTANTS
EQS
AA-EQS(3) AA-EQS(3) MAC-EQS(5) MAC-EQS(5) Biota(6)
Entry Inland surface Other surface Inland surface Other surface [μg/kg wet weight] or
Name of substance Category of substances CAS number(1) EU number(2)
No waters(4) waters waters(4) waters EQS Sediment where
[μg/l] [μg/l] [μg/l] [μg/l] so indicated [μg /kg
dry weight]
1 Alachlor(7) Pesticides 15972-60-8 240-110-8 0,3 0,3 0,7 0,7
2 Carbon tetrachloride(7) Industrial substances 56-23-5 200-262-8 12 12 not applicable not applicable
3 Chlorfenvinphos(7) Pesticides 470-90-6 207-432-0 0,1 0,1 0,3 0,3
4 Simazine(7) Pesticides 122-34-9 204-535-2 1 1 4 4
5 Trichlorobenzenes(7) Industrial 12002-48-1 234-413-4 0,4 0,4 not applicable not applicable
substances –
solvent
6 Atrazine(7) Pesticides – 1912-24-9 217-617-8 0,6 0,6 2,0 2,0
herbicides
(1) CAS: Chemical Abstracts Service.
(2) EU number: European Inventory of Existing Commercial Substances (EINECS) or European List of Notified Chemical Substances (ELINCS).
(3) This parameter is the EQS expressed as an annual average value (AA-EQS). Unless otherwise specified, it applies to the total concentration of all substances and isomers.
(4) Inland surface waters encompass rivers and lakes and related artificial or heavily modified water bodies.
(5) This parameter is the EQS expressed as a maximum allowable concentration (MAC EQS). Where the MAC EQS are marked as “not applicable”, the AA EQS values are considered protective against short-term
pollution peaks in continuous discharges since they are significantly lower than the values derived on the basis of acute toxicity.
(6) If a biota EQS is given, it, rather than the water EQS, shall be applied, without prejudice to Article 3(3) of this Directive allowing an alternative biota taxon, or another matrix, to be monitored instead, as long as the
EQS applied provides an equivalent level of protection. Unless otherwise indicated, the biota EQS relate to fish.
(7) Substance previously listed as a priority substance in Annex X to Directive 2000/60/EC or Annex I to Directive 2008/105/EC.’.
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ANNEX VIII
The following Annex is added in Directive 2008/105/EC
‘ANNEX III
SUBSTANCES SUBJECT TO REVIEW FOR POSSIBLE IDENTIFICATION AS PRIORITY SUBSTANCES
Name of substance CAS number(1) EU number(2)
Sum of Bisphenols not applicable not applicable
Sum(s) of selected pesticides by mode of not applicable not applicable
action
Sum(s) of selected pharmaceuticals by not applicable not applicable
mode of action
(1) CAS: Chemical Abstracts Service.
(2) EU number: European Inventory of Existing Commercial Substances (EINECS) or European List of Notified Chemical Substances
(ELINCS).’.
84/84 ELI: http://data.europa.eu/eli/dir/2026/805/oj