ANNEXES to the Proposal for a Directive of the European Parliament and of the Council 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 - Hoofdinhoud

Document­datum	31-10-2022
Publicatie­datum	01-11-2022
Kenmerk	14265/22 ADD 1
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Originele document in PDF

Council of the European Union

Brussels, 31 October 2022 (OR. en)

14265/22

Interinstitutional File: ADD 1

2022/0344(COD) i

ENV 1092 CLIMA 558 AGRI 600 FORETS 110 ENER 553 TRANS 677 CODEC 1645

COVER NOTE

From: Secretary-General of the European Commission, signed by Ms Martine DEPREZ, Director

date of receipt: 27 October 2022

To: Ms Thérèse BLANCHET, Secretary-General of the Council of the

European Union

No. Cion doc.: COM(2022) 540 final i - ANNEXES 1 to 6

Subject: ANNEXES to the Proposal for a Directive of the European Parliament and of the Council amending Directive 2000/60/EC i establishing a

framework for Community action in the field of water policy, Directive 2006/118/EC i on the protection of groundwater against pollution and deterioration and Directive 2008/105/EC i on environmental quality standards in the field of water policy

Delegations will find attached document COM(2022) 540 final i - ANNEXES 1 to 6.

Encl.: COM(2022) 540 final i - ANNEXES 1 to 6

EUROPEAN COMMISSION

Brussels, 26.10.2022 COM(2022) 540 final i

ANNEXES 1 to 6

ANNEXES

to the

Proposal for a Directive of the European Parliament and of the Council

amending Directive 2000/60/EC i establishing a framework for Community action in the field of water policy, Directive 2006/118/EC i on the protection of groundwater against pollution and deterioration and Directive 2008/105/EC i on environmental quality

standards in the field of water policy

{SEC(2022) 540 final} - {SWD(2022) 540 final} - {SWD(2022) 543 final} ANNEX I

Annex V to Directive 2000/60/EC i is amended as follows:

• (1) 

  points 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

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

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.’;

• (2) 

  in point 1.2.1, the table ‘Physio-chemical quality elements’ is replaced by the following:

‘General physico-chemical quality elements

Element High status Good status Moderate status

General The values of the general Temperature, oxygen Conditions consistent with conditions physico-chemical elements balance, pH, acid the achievement of the

correspond totally or nearly neutralising capacity and values specified above for totally to undisturbed salinity do not reach levels the biological quality

conditions. outside the range elements.’;

Nutrient established so as to ensure concentrations the functioning of the type

remain within the range specific ecosystem and the

normally associated with

undisturbed conditions. achievement of the values specified above for the

Levels of salinity, pH, biological quality elements.

oxygen balance, acid Nutrient concentrations do

neutralising capacity and not exceed the levels

temperature do not show

signs of established so as to ensure anthropogenic

disturbance and the functioning of the remain ecosystem

within the range normally and the

achievement of the values associated with undisturbed

conditions. specified above for the biological quality elements.

• (3) 

  in point 1.2.2, the table ‘Physio-chemical quality elements’ is replaced by the following:

‘General physico-chemical quality elements

Element High status Good status Moderate status

General The values of the general Temperature, oxygen Conditions consistent with conditions physico-chemical elements balance, pH, acid the achievement of the

correspond totally or nearly neutralising capacity, values specified above for totally to undisturbed transparency and salinity do the biological quality

conditions. not reach levels outside the elements.’;

Nutrient range established so as to concentrations ensure the functioning of the

remain within the range ecosystem

normally associated with and the

undisturbed conditions. achievement of the values specified above for the

Levels of salinity, pH, biological quality elements.

oxygen balance, acid

neutralising Nutrient concentrations do capacity,

transparency not exceed the levels and established so as to ensure

temperature do not show

signs of the functioning of the anthropogenic

disturbance ecosystem and remain and the achievement of the values

within the range normally specified above for the

associated with undisturbed

conditions. biological quality elements.

• (4) 

  in point 1.2.3, the table ‘Physio-chemical quality elements’ is replaced by the following:

‘General physico-chemical quality elements

Element High status Good status Moderate status

General The general physico Temperature, oxygenation Conditions consistent with conditions chemical elements conditions and transparency the achievement of the

correspond totally or do not reach levels outside values specified above for nearly totally to the ranges established so as the biological quality

undisturbed conditions. to ensure the functioning of elements.’;

Nutrient the ecosystem and the concentrations achievement of the values

remain within the range specified above for the

normally associated with

undisturbed conditions. biological quality elements.

Temperature, Nutrient concentrations do oxygen not exceed the levels

balance and transparency established so as to ensure

do not show signs of the functioning of the

anthropogenic disturbance ecosystem

and remain within the and the

achievement of the values range normally associated

with specified above for the undisturbed conditions. biological quality elements.

• (5) 

  in point 1.2.4, the table ‘Physio-chemical quality elements’ is replaced by the following:

  ‘General physico-chemical quality elements Element High status Good status Moderate status

General The general physico Temperature, oxygenation Conditions consistent with conditions chemical elements conditions and transparency the achievement of the

correspond totally or do not reach levels outside values specified above for nearly totally to the ranges established so as the biological quality

undisturbed conditions. to ensure the functioning of elements.’;

Nutrient the ecosystem and the concentrations achievement of the values

remain within the range specified above for the

normally associated with

undisturbed conditions. biological quality elements.

Temperature, Nutrient concentrations do oxygen not exceed the levels

balance and transparency established so as to ensure

do not show signs of the functioning of the

anthropogenic disturbance ecosystem

and remain within the and the

achievement of the values ranges normally associated

with specified above for the undisturbed conditions. biological quality elements.

• (6) 

  in point 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) 

  point 1.2.6 is deleted;

• (8) 

  in point 1.3, the following fourth and fifth 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 points.

  Member States may apply passive sampling methods to monitor chemical pollutants, where appropriate, in particular for screening purposes, 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 sampling methods subject to the same conditions.’;

• (9) 

  in point 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 coverthe 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 list pollutants which are discharged or otherwise deposited into the river basin or sub-basin;

(e) other pollutants discharged or otherwise deposited in significant quantities in the river basin or sub-basin.

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.’;

• (10) 

  point 1.3.2. is amended as follows:

  ‘(a) in the third paragraph, ’Selection of monitoring sites’, the first sentence 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 list substances are discharged or otherwise deposited or into which river basin specific pollutants are discharged or otherwise

deposited in significant quantities.;

(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 point 1.3.4, the table, the sixth row under the heading ‘Physico-chemical’, the words ’Other pollutants’ are replaced by ‘River basin specific pollutants’;

• (12) 

  point 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

delegated act in accordance with Article 20.’;

• (13) 

  in point 1.4.2, point (iii) is deleted;

• (14) 

  in point 1.4.3, the first paragraph, the first sentence is replaced by the following:

‘A body of water shall be recorded as achieving good chemical status where it is compliant with all the environmental quality standards set out in Part A of Annex I to Directive 2008/105/EC i and the environmental quality standards established pursuant

to Articles 8 and 8d of that Directive.’;

• (15) 

  in point 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.’;

• (16) 

  point 2.3.2. is replaced by the following:

‘2.3.2. Definition of good groundwater chemical status

Elements Good status

General 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 i, the threshold values for groundwater pollutants and indicators of pollution set pursuant to Article 3(1), point (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’;

• (17) 

  in point 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.’;

• (18) 

  point 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 i;

(b) chemical parameters for which national thresholds have been set pursuant to Article 3(1), point (b), of Directive 2006/118/EC i;

(c) chemical parameters for which Union wide thresholds have been set

pursuant to Article 8(3) of Directive 2006/118/EC i.

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 point 2.5, Member States shall provide a map of groundwater chemical status, colour-coded as follows:

Good: green

Poor: red

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 a trend shall be indicated by a blue dot on the map.

These maps shall be included in the river basin management plans.’.

ANNEX II

Annex VIII of Directive 2000/60/EC i is amended as follows:

• (1) 

  point 10 is replaced by the following:

  ‘10. Materials in suspension, including micro/nanoplastics.’;

• (2) 

  point 13 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.’.

ANNEX III

‘ANNEX I

GROUNDWATER QUALITY STANDARDS (QS)

Note 1: The QS for the pollutants listed under entries 3 to 7 shall apply from … [OP: please insert the date = the first day of the month following 18 months after the entry into force of this amending Directive], with the aim of achieving good water chemical status at the latest by 22 December 2033.

(1 (5)

) (2) (3) (4) (6)

[E Name of Category of CAS number EU number Quality Standard ( 3 )

ntr substance substances ( 1 ) ( 2 )

y] [µg/l unless otherwise N o indicated]

1 Nitrates Nutrients not not applicable 50 mg/l applicable

2 Active Pesticides not not applicable 0,1 (individual) substances in applicable

pesticides, including their relevant

metabolites, 0,5 (total) (

5 )

degradation and reaction

products 4 ( )

3 Per- and poly Industrial See table See table note 0,0044 ( 7 )

fluorinated alkyl substances note 6 6 substances (PFAS) - sum of 24 ( 6 )

4 Carbamazepine Pharmaceuticals 298-46-4 not applicable 0,25

5 Sulfamethoxazol Pharmaceuticals 723-46-6 not applicable 0,01 e

6 Pharmaceutical Pharmaceuticals not not applicable 0,25 active applicable

substances –

(1

) (2) (3) (4)

• (5) 

  (6)

total ( 8 )

7 Non-relevant Pesticides not not applicable 0,1 ( 9 ) or 1 ( 10 ) or 2,5 metabolites of applicable or 5 ( 11 ) (individual)

pesticides

(nrMs) 0,5 ( 9 ) or 5 ( 10 ) or

12,5 ( 11 ) (total) ( 12 )

( 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 i of the European Parliament and of the Council of 21 October 2009 concerning the placing of plant protection products on the market and in Article 3 of Regulation (EU) No 528/2012 i of the European Parliament and of the Council of 22 May 2012 concerning the making available on the market and use of biocidal products, respectively.

( 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 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), Ammonium perfluoro (2-methyl-3-oxahexanoate) (HFPO-DA or Gen X) (CAS 62037-80-3) (RPF 0,06), Propanoic Acid / Ammonium 2,2,3-trifluoro-3-(1,1,2,2,3,3-hexafluoro-3- (trifluoromethoxy)propoxy)propanoate (ADONA) (CAS 958445-44-8) (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 Acetic acid / 2,2-difluoro-2-((2,2,4,5-tetrafluoro-5- (trifluoromethoxy)-1,3-dioxolan-4-yl)oxy)- (C6O4) (CAS 1190931-41-9) (RPF 0,06).

( 7 ) The QS refers to the sum of the 24 PFAS listed in footnote 6 expressed as PFOA-equivalents based on the potencies of the substances relative to that of PFOA, i.e. the RPFs in footnote 6.

( 8 ) ‘Total’ means the sum of all individual pharmaceuticals detected and quantified in the monitoring procedure, including relevant metabolites and degradation products.

( 9 ) Applicable to ‘data-poor’ nrMs, i.e. nrMs for which no reliable experimental data on chronic or acute effects of the nrM are available on the taxonomic group confidently predicted to be the most sensitive.

( 10 ) Applicable to ‘data-fair’ nrMs, i.e. nrMs for which reliable experimental data on chronic or acute effects of the nrM are available on the taxonomic group confidently predicted to be the most sensitive, but where the data are insufficient to qualify the substances as ‘data-rich’.

( 11 ) Applicable to ‘data-rich’ nrMs, i.e. nrMs for which reliable experimental data, or equally reliable data obtained by alternative scientifically validated methods, are available on chronic or acute effects of the nrM on at least one species each of algae, of invertebrates, and of fish, allowing the most-sensitive taxonomic group to be confidently confirmed, and for which a QS can be calculated using a deterministic approach based on reliable chronic experimental toxicity data on that taxonomic group; Member States may apply for this purpose the latest guidance established in the framework of the Common Implementation Strategy for Directive 2000/60/EC i (Guidance document No. 27, as updated). The QS of 2,5 for individual nrMs shall apply unless the QS calculated by the deterministic approach is higher, in which case a QS of 5 shall apply.

( 12 ) ‘Total’ means the sum of all individual nrMs in each data category detected and quantified in the monitoring procedure.

ANNEX IV

Annex II of Directive 2006/118/EC i is amended as follows:

• (1) 

  in part A, the following paragraph is inserted after the first paragraph:

‘Member States shall ensure that competent authorities inform the European Chemicals Agency ECHA of threshold values for pollutants and indicators of

pollution. ECHA shall publish that information without delay.’;

• (2) 

  in part B, point 2 is replaced by the following:

‘2. Man-made synthetic substances

Primidone

Trichloroethylene

Tetrachloroethylene’

• (3) 

  in Part C, the title is replaced by the following:

‘Information to be provided by Member States with regard to the pollutants and their indicators for which threshold values have been established by the Member States’;

• (4) 

  the following Part D is added:

  ‘Part D

  Repository of harmonised threshold values for groundwater pollutants of

  national, regional or local concern

• (1) 

  (2) (3) (4) (5) (6)

[Entry] Name of substance Category of CAS EU Threshold value N o substances number (1) number (2)

[µg/l unless otherwise indicated]

1 Trichloroethylene Industrial 79-01-6 201-167-4 10 (total) ( 3 )

and substances and and 204- Tetrachloroethylene 127-18-4 825-9 (sum 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 ) ‘Total’ means the sum of concentrations of Trichloroethylene and Tetrachloroethylene

ANNEX V

Annex I to Directive 2008/105/EC i is amended as follows:

• (1) 

  the title is replaced by the following:

  ‘ENVIRONMENTAL QUALITY STANDARDS (EQS) FOR PRIORITY SUBSTANCES IN SURFACE WATERS’;

• (2) 

  Part A is replaced by the following:

  ‘PART A: ENVIRONMENTAL QUALITY STANDARDS

Note 1: Where an EQS is listed between [], this value is subject to confirmation in the light of the opinion requested from the Scientific Committee on Health, Environmental and Emerging Risks.

• (1) 

  (2) (3) (4) (5) (6) (7) (8) (9) (10) (11) (12) (13) [Entry Name of substance Category of CAS EU number AA-EQS ( 3 ) AA-EQS ( 3 ) MAC-EQS MAC-EQS EQS Identified as Identified as Identified ] N° substances number ( 1 ) ( 2 ) Inland

  surface Other surface

  ( 5 ) ( 5 ) Biota ( 6 ) a priority an as a

  waters ( 4 ) waters Inland Other

hazardous Ubiquitous substance

surface surface [µg/kg wet substance Persistent, that tends

waters ( 4 ) waters weight] Bioaccumul to

[µg/l] [µg/l] or EQS ative and accumulat Sediment Toxic e in

[µg/l] [µg/l] [µg /kg dry (uPBT) sediment weight] substance and/or

where so biota indicated

• (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) 

  Atrazine Herbicides 1912-24-9 217-617-8 0,6 0,6 2,0 2,0

• (4) 

  Benzene Industrial 71-43-2 200-753-7 10 8 50 50 substances

• (5) 

  Brominated Industrial not not 0,14 ( 7 ) 0,014 ( 7 ) [0,00028] X ( 8 ) X X diphenylethers substances applicable applicable ( 7 )

• (6) 

  Cadmium and its Metals 7440-43-9 231-152-8 ≤ 0,08 (Class 0,2 ≤ 0,45 (Class ≤ 0,45 (Class X X compounds 1) 1) 1)

  (depending on water 0,08 (Class 0,45 (Class 0,45 (Class hardness classes) ( 9 ) 2) 2) 2)

  0,09 (Class 0,6 (Class 3) 0,6 (Class 3)

  • 3) 

    0,9 (Class 4) 0,9 (Class 4)

  0,15 (Class

  • 4) 

    1,5 (Class 5) 1,5 (Class 5)

  0,25 (Class 5)

(6a) The substance Carbon tetrachloride has been moved to Part C of Annex II

• (7) 

  C 10-13 Chloroalkanes ( 10 ) Industrial 85535-84- 287-476-5 0,4 0,4 1,4 1,4 X X substances 8

• (8) 

  The substance Chlorfenvinphos has been moved to Part C of Annex II

• (9) 

  Chlorpyrifos Organophosp 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) hate pesticides

(9a) Cyclodiene pesticides: Organochlori Σ = 0,01 Σ = 0,005 not not X

Aldrin ne pesticides 309-00-2 206-215-8 applicable applicable

Dieldrin 60-57-1 200-484-5

Endrin 72-20-8 200-775-7

Isodrin 465-73-6 207-366-2

(9b) DDT total ( 11 ) Organochlori not not 0,025 0,025 not not X ne pesticides applicable applicable applicable applicable

para-para-DDT 50-29-3 200-024-3 0,01 0,01 not not X applicable applicable

• (10) 

  1,2-Dichloroethane Industrial 107-06-2 203-458-1 10 10 not not X substances applicable applicable

• (11) 

  Dichloromethane Industrial 75-09-2 200-838-9 20 20 not not substances applicable applicable

• (12) 

  Di(2-ethylhexyl)- Industrial 117-81-7 204-211-0 1,3 1,3 not not X X phthalate (DEHP) substances applicable applicable

• (13) 

  Diuron Herbicides 330-54-1 206-354-4 0,049 0,0049 0,27 0,054

• (14) 

  Endosulfan Organochlori 115-29-7 204-079-4 0,005 0,0005 0,01 0,004 X ne pesticides

• (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

  ne pesticides

EN 18 EN

• (17) 

  Hexachlorobutadiene Industrial 87-68-3 201-765-5 9 × 10 -4 0,6 0,6 21 X X substances

  (solvents)

• (18) 

  Hexachlorocyclohexane Insecticides 608-73-1 210-168-9 0,02 0,002 0,04 0,02 X X

• (19) 

  Isoproturon Herbicides 34123-59- 251-835-4 0,3 0,3 1,0 1,0

  6

• (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 [10] ( 13 ) X X X compounds

• (22) 

  Naphthalene Industrial 91-20-3 202-049-5 2 2 130 130 substances

• (23) 

  Nickel and its Metals 7440-02-0 231-111-4 2 ( 12 ) 3,1 8,2 8,2 compounds

• (24) 

  Nonylphenols ( 14 ) Industrial 84852-15- 284-325-5 0,037 0,0018 2,1 0,17 X

  (4-Nonylphenol) substances 3

• (25) 

  Octylphenols ( 15 ) Industrial 140-66-9 205-426-2 0,1 0,01 not not X

  ((4-(1,1',3,3'- substances applicable applicable tetramethylbutyl)- phenol))

• (26) 

  Pentachlorobenzene Industrial 608-93-5 210-172-0 0,007 0,0007 not not X X substances applicable applicable

• (27) 

  Pentachlorophenol Organochlori 87-86-5 201-778-6 0,4 0,4 1 1 X ne pesticides

• (28) 

  Polyaromatic Combustion not not not not not not Sum of X X X hydrocarbons (PAHs) products applicable applicable applicable applicable applicable applicable Benzo(a)py

  16

  ( ) rene equivalents [0.6] ( 17 )

  Benzo(a)pyrene 50-32-8 200-028-5 0,27 0,027 [0,6] Benzo(b)fluoranthene 205-99-2 205-911-9 0,017 0,017 see footnote 17

  Benzo(k)fluoranthene 207-08-9 205-916-6 0,017 0,017 see footnote 17

  Benzo(g,h,i)perylene 191-24-2 205-883-8 8,2 × 10 -3 8,2 × 10 -4 see footnote

  17

  Indeno(1,2,3-cd)pyrene 193-39-5 205-893-2 not not see footnote applicable applicable 17

  Chrysene 218-01-9 205-923-4 0,07 0,007 see footnote 17

  Benzo(a)anthracene 56-55-3 200-280-6 0,1 0,01 see footnote 17

  Dibenz(a,h)anthracene 53-70-3 200-181-8 0,014 0,0014 see footnote 17

• (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 not substances applicable applicable

(29b) Trichloroethylene Industrial 79-01-6 201-167-4 10 10 not not X substances applicable applicable

• (30) 

  Tributyltin compounds Biocides 36643-28- not 0,0002 0,0002 0,0015 0,0015 [1,3] ( 19 ) X X X (

  18 ) (Tributyltin-cation) 4 applicable

• (31) 

  Trichlorobenzenes Industrial 12002-48- 234-413-4 0,4 0,4 not not substances 1 applicable applicable (solvents)

• (32) 

  Trichloromethane Industrial 67-66-3 200-663-8 2,5 2,5 not not substances applicable applicable

• (33) 

  Trifluralin Herbicides 1582-09-8 216-428-8 0,03 0,03 not not X applicable applicable

• (34) 

  Dicofol Organochlori 115-32-2 204-082-0 [4,45 × 10 -3 ] [0,185 × 10 -3 ] not not [5.45] X X ne pesticides applicable applicable

  ( 20 ) ( 20 )

• (35) 

  Perfluorooctane sulfonic Industrial 1763-23-1 217-179-8 Coverd by substance group 65 (Per- and poly-fluorinated alkyl substances (PFAS) – sum of 24) acid and its derivatives substances

  (PFOS)

• (36) 

  Quinoxyfen Plant 124495- not 0,15 0,015 2,7 0,54 X X protection 18-7 applicable

  products

• (37) 

  Dioxins and dioxin-like Industrial not not not not Sum of X X X compounds ( 21 ) byproducts applicable applicable applicable applicable PCDDs+

  PCDFs+ PCB-DLs

  equivalents [3,5 10 -5 ] ( 22 )

• (38) 

  Aclonifen Herbicides 74070-46- 277-704-1 0,12 0,012 0,12 0,012 5

• (39) 

  Bifenox Herbicides 42576-02- 255-894-7 0,012 0,0012 0,04 0,004 3

• (40) 

  Cybutryne Biocides 28159-98- 248-872-3 0,0025 0,0025 0,016 0,016 0

• (41) 

  Cypermethrin ( 23 ) Pyrethroid 52315-07- 257-842-9 3 × 10 -5 3 × 10 -6 6 × 10 -4 6 × 10 -5 X pesticides 8

• (42) 

  Dichlorvos Organophosp 62-73-7 200-547-7 6 × 10 -4 6 × 10 -5 7 × 10 -4 7 × 10 -5 hate

  pesticides

• (43) 

  Hexabromocyclododeca Industrial See See [4,6 × 10 -4 ] [2 × 10 -5 ] 0,5 0,05 [3,5] X X X ne (HBCDD) ( 24 ) substances footnote footnote

  24 24 (44) Heptachlor and Organochlori 76-44-8 / 200-962- [1,7 × 10 -7 ] [1,7 × 10 -7 ] 3 × 10 -4 3 × 10 -5 [0,013] X X X

  heptachlor epoxide ne pesticides 1024-57-3 3/ 213- 831-0

• (45) 

  Terbutryn Herbicides 886-50-0 212-950-5 0,065 0,0065 0,34 0,034

• (46) 

  17 alpha-ethinylestradiol Pharmaceutic 57-63-6 200-342-2 1,7 × 10 -5 1,6 × 10 -6 not derived not derived

  (EE2) als (Estrogenic hormones)

• (47) 

  17 beta-estradiol (E2) Pharmaceutic 50-28-2 200-023-8 0,00018 9 × 10 -6 not derived not derived als

  (Estrogenic hormones)

• (48) 

  Acetamiprid Neonicotinoid 135410- 603-921-1 0,037 0,0037 0,16 0,016 pesticides 20-7 /

  160430- 64-8

• (49) 

  Azithromycin Pharmaceutic 83905-01- 617-500-5 0,019 0,0019 0,18 0,018 X als 5

  (Macrolide antibiotics)

• (50) 

  Bifenthrin Pyrethroid 82657-04- 617-373-6 9,5 × 10 -5 9,5 × 10 -6 0,011 0,001 X pesticides 3

• (51) 

  Bisphenol-A (BPA) Industrial 80-05-7 201-245-8 3,4 × 10 -5 3,4 × 10 -5 130 51 0,005 X substances

• (52) 

  Carbamazepine Pharmaceutic 298-46-4 206-062-7 2,5 0,25 1,6 × 10 3 160 als

• (53) 

  Clarithromycin Pharmaceutic 81103-11- 658-034-2 0,13 0,013 0,13 0,013 X als 9

  (Macrolide antibiotics)

• (54) 

  Clothianidin Neonicotinoid 210880- 433-460-1 0,01 0,001 0,34 0,034 pesticides 92-5

• (55) 

  Deltamethrin Pyrethroid 52918-63- 258-256-6 1,7 × 10 -6 1,7 × 10 -7 1,7 × 10 -5 3,4 × 10 -6 X pesticides 5

• (56) 

  Diclofenac Pharmaceutic 15307-86- 239-348-5 0,04 0,004 250 25 X als 5 / 15307- / 239-

  79-6 346-4

• (57) 

  Erythromycin Pharmaceutic 114-07-8 204-040-1 0,5 0,05 1 0,1 X als

  (Macrolide antibiotics)

• (58) 

  Esfenvalerate Pyrethroid 66230-04- 613-911-9 1,7 × 10 -5 1,7 × 10 -6 0,0085 0,00085 X pesticides 4

• (59) 

  Estrone (E1) Pharmaceutic 53-16-7 200-164-5 3,6 × 10 -4 1,8 × 10 -5 not derived not derived als

  (Estrogenic hormones)

• (60) 

  Glyphosate Herbicides 1071-83-6 213-997-4 0,1 ( 25 ) 8,67 398,6 39,86

  86,7 ( 26 )

• (61) 

  Ibuprofen Pharmaceutic 15687-27- 239-784-6 0,22 0,022 X als 1

• (62) 

  Imidacloprid Neonicotinoid 138261- 428-040-8 0,0068 6,8 × 10 -4 0,057 0,0057 pesticides 41-3 /

  105827- 78-9

• (63) 

  Nicosulfuron Herbicides 111991- 601-148-4 0,0087 8,7 × 10 -4 0,23 0,023

  09-4

• (64) 

  Permethrin Pyrethroid 52645-53- 258-067-9 2,7× 10 -4 2.7 × 10 -5 0,0025 2,5 × 10 -4 X pesticides 1

• (65) 

  Per- and poly-fluorinated Industrial not not Sum of Sum of not not Sum of X X X alkyl substances (PFAS) substances applicable applicable PFOA PFOA applicable applicable PFOA

  – sum of 24 ( 27 ) equivalents equivalents equivalents 0,0044 ( 28 ) 0,0044 ( 28 ) 0,077 ( 28 )

• (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 Neonicotinoid 111988- 601-147-9 0,01 0,001 0,05 0,005 pesticides 49-9

• (68) 

  Thiamethoxam Neonicotinoid 153719- 428-650-4 0,04 0,004 0,77 0,077 pesticides 23-4

• (69) 

  Triclosan Biocides 3380-34-5 222-182-2 0,02 0,002 0,02 0,002

• (70) 

  Total of active Plant 0,5 ( 30 ) 0,5 ( 30 ) substances in pesticides, protection

  including their relevant products and metabolites, degradation biocides and reaction products

  29

  ( )

  ( 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 an EQS biota is given, it, rather than the water EQS, shall be applied, without prejudice to the provision in 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. 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 and 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 Commission Regulation (EU) No 1259/2011 i* Annex Section 5.3. ( 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 CaCO3/l, Class 2: 40 to <50 mg CaCO3/l, Class 3: 50 to <100 mg CaCO3/l, Class 4: 100 to <200 mg CaCO3/l and Class 5: ≥200 mg CaCO3/l). ( 10 ) No indicative parameter is provided for this group of substances. The indicative parameter(s) must 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. ( 13 ) The EQS for biota refers to methyl mercury. ( 14 )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). ( 15 )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). ( 16 ) 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), and dibenz(a,h)anthracene (CAS 53-70-3) (RPF 1). The PAHs anthracene, fluoranthene and naphthalene are listed separately. ( 17 )For the group of polyaromatic hydrocarbons (PAHs) (No 28), the biota EQS refers to the sum of the concentrations of seven of the eight PAHs listed in footnote 17 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 16. Benzo(g,h,i)perylene does not need to be measured in biota for the purposes of determining compliance with the overall EQS biota. ( 18 )Tributyltin compounds including tributyltin-cation (CAS 36643-28-4). ( 19 )Sediment EQS ( 20 )There is insufficient information available to set a MAC-EQS for these substances. ( 21 )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). ( 22 )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. ( 23 )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 52315-07-8, EU 257-842-9). ( 24 )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).

EN 25 EN

( 26 )For freshwater not used for the abstraction and preparation of drinking water.

( 27 )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), and Ammonium perfluoro (2-methyl-3-oxahexanoate) (HFPO-DA or Gen X) (CAS 62037-80-3) (RPF 0,06), Propanoic Acid / Ammonium 2,2,3-trifluoro-3-(1,1,2,2,3,3-hexafluoro 3-(trifluoromethoxy)propoxy)propanoate (ADONA) (CAS 958445-44-8) (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 Acetic acid / 2,2-difluoro-2-((2,2,4,5-tetrafluoro-5-(trifluoromethoxy)-1,3-dioxolan-4- yl)oxy)- (C6O4) (CAS 1190931-41-9) (RPF 0,06)

( 28 ) For the group of PFAS (No 65), the EQS refer to the sum of the concentrations of the 24 PFAS listed in footnote 27 expressed as PFOA-equivalents based on the potencies of the substances relative to that of PFOA, i.e. the RPFs in footnote 27.

( 29 ) ‘Pesticides’ means plant protection products as referred to in Article 2 of Regulation (EC) No 1107/2009and biocidal products as defined in Article 3 of Regulation (EU) No 528/2012 i.

( 30 ) ‘Total’ means the sum of all individual pesticides detected and quantified in the monitoring procedure, including their relevant metabolites, degradation and reaction products.’;

• (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.’.

ANNEX VI

‘ANNEX II

ENVIRONMENTAL QUALITY STANDARDS FOR RIVER BASIN SPECIFIC POLLUTANTS

P ART A: 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. 

  Substances which contribute to eutrophication (in particular, nitrates and

phosphates).

• 12. 

  Substances which have an unfavourable influence on the oxygen balance and can be measured using parameters such as BOD, COD, etc.

• 13. 

  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.

PART C: REPOSITORY OF HARMONISED ENVIRONMENTAL QUALITY STANDARDS FOR RIVER BASIN SPECIFIC POLLUTANTS

[En Name of Category of CAS EU AA- AA- MAC- MAC- EQS try] substance substances number number EQS EQS EQS EQS N° ( 1 ) ( 2 ) ( 3 ) ( 3 ) ( 5 ) ( 5 )

Biota ( 6

Inlan Othe Inland Other [µg/kg d r surfac surfac wet surfa surfa e e weight] ce ce waters waters or EQS water water ( 4 ) Sedimen

s ( 4 ) s [µg/l] t where so

[µg/l [µg/l indicate

] ] [µg/l] d [µg

/kg dry weight]

1 Alachlor Pesticides 15972-60- 240- 0,3 0,3 0,7 0,7

( 7 ) 8 110-8

2 Carbon Industrial 56-23-5 200- 12 12 not not tetrachlorid substances 262-8 applic applic e ( 7 ) able able

3 Chlorfenvi Pesticide 470-90-6 207- 0,1 0,1 0,3 0,3 nphos ( 7 ) 432-0

4 Simazine Pesticide 122-34-9 204- 1 1 4 4

7

( ) 535-2

( 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 the provision in 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 i or Annex I to Directive 2008/105/EC i.’.