EUROPEAN COMMISSION
Brussels, 26.10.2022
COM(2022) 540 final
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
{SEC(2022) 540 final} - {SWD(2022) 540 final} - {SWD(2022) 543 final}
ANNEX I
Annex V to Directive 2000/60/EC 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 conditions
|
The values of the general physico-chemical elements correspond totally or nearly totally to undisturbed conditions.
Nutrient concentrations remain within the range normally associated with undisturbed conditions.
Levels of salinity, pH, oxygen balance, acid neutralising capacity and temperature do not show signs of anthropogenic disturbance and remain within the range normally associated with undisturbed conditions.
|
Temperature, oxygen balance, pH, acid neutralising capacity and salinity do not reach levels outside the range established so as to ensure the functioning of the type specific ecosystem and the achievement of the values specified above for the biological quality elements.
Nutrient concentrations do not exceed the levels established so as to ensure the functioning of the ecosystem and the achievement of the values specified above for the biological quality elements.
|
Conditions consistent with the achievement of the values 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 conditions
|
The values of the general physico-chemical elements correspond totally or nearly totally to undisturbed conditions.
Nutrient concentrations remain within the range normally associated with undisturbed conditions.
Levels of salinity, pH, oxygen balance, acid neutralising capacity, transparency and temperature do not show signs of anthropogenic disturbance and remain within the range normally associated with undisturbed conditions.
|
Temperature, oxygen balance, pH, acid neutralising capacity, transparency and salinity do not reach levels outside the range established so as to ensure the functioning of the ecosystem and the achievement of the values specified above for the biological quality elements.
Nutrient concentrations do not exceed the levels established so as to ensure the functioning of the ecosystem and the achievement of the values specified above for the biological quality elements.
|
Conditions consistent with the achievement of the values specified above for the 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 conditions
|
The general physico-chemical elements correspond totally or nearly totally to undisturbed conditions.
Nutrient concentrations remain within the range normally associated with undisturbed conditions.
Temperature, oxygen balance and transparency do not show signs of anthropogenic disturbance and remain within the range normally associated with undisturbed conditions.
|
Temperature, oxygenation conditions and transparency do not reach levels outside the ranges established so as to ensure the functioning of the ecosystem and the achievement of the values specified above for the biological quality elements.
Nutrient concentrations do not exceed the levels established so as to ensure the functioning of the ecosystem and the achievement of the values specified above for the biological quality elements.
|
Conditions consistent with the achievement of the values specified above for the 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 conditions
|
The general physico-chemical elements correspond totally or nearly totally to undisturbed conditions.
Nutrient concentrations remain within the range normally associated with undisturbed conditions.
Temperature, oxygen balance and transparency do not show signs of anthropogenic disturbance and remain within the ranges normally associated with undisturbed conditions.
|
Temperature, oxygenation conditions and transparency do not reach levels outside the ranges established so as to ensure the functioning of the ecosystem and the achievement of the values specified above for the biological quality elements.
Nutrient concentrations do not exceed the levels established so as to ensure the functioning of the ecosystem and the achievement of the values specified above for the biological quality elements.
|
Conditions consistent with the achievement of the values specified above for the 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 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, 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;
(b) chemical parameters for which national thresholds have been set pursuant to Article 3(1), point (b), of Directive 2006/118/EC;
(c) chemical parameters for which Union wide thresholds 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 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 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)
|
(2)
|
(3)
|
(4)
|
(5)
|
(6)
|
|
[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, including their relevant metabolites, degradation and reaction products (4)
|
Pesticides
|
not applicable
|
not applicable
|
0,1 (individual)
|
|
|
|
|
|
|
0,5 (total) (5)
|
|
3
|
Per- and poly-fluorinated alkyl substances (PFAS) - sum of 24 (6)
|
Industrial substances
|
See table note 6
|
See table note 6
|
0,0044 (7)
|
|
4
|
Carbamazepine
|
Pharmaceuticals
|
298-46-4
|
not applicable
|
0,25
|
|
5
|
Sulfamethoxazole
|
Pharmaceuticals
|
723-46-6
|
not applicable
|
0,01
|
|
6
|
Pharmaceutical active substances – total (8)
|
Pharmaceuticals
|
not applicable
|
not applicable
|
0,25
|
|
7
|
Non-relevant metabolites of pesticides (nrMs)
|
Pesticides
|
not applicable
|
not applicable
|
0,1 (9) or 1 (10) or 2,5 or 5 (11) (individual)
|
|
|
|
|
|
|
0,5 (9) or 5 (10) or 12,5 (11) (total) (12)
|
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:
‘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] No
|
Name of substance
|
Category of substances
|
CAS number(1)
|
EU number(2)
|
Threshold value
[µg/l unless otherwise indicated]
|
|
1
|
Trichloroethylene and Tetrachloroethylene (sum of two)
|
Industrial substances
|
79‑01‑6 and 127‑18‑4
|
201-167-4 and 204-825-9
|
10 (total)(3)
|
ANNEX V
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’;
(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] N°
|
Name of substance
|
Category of substances
|
CAS number (1)
|
EU number (2)
|
AA‑EQS (3) Inland surface waters (4)
[µg/l]
|
AA‑EQS (3)
Other surface waters
[µg/l]
|
MAC‑EQS (5)
Inland surface waters (4)
[µg/l]
|
MAC‑EQS (5)
Other surface waters
[µg/l]
|
EQS
Biota (6)
[µg/kg wet weight]
or EQS Sediment [µg /kg dry weight] where so indicated
|
Identified as a priority hazardous substance
|
Identified as an Ubiquitous Persistent, Bioaccumulative and Toxic (uPBT) substance
|
Identified as a substance that tends to accumulate in sediment and/or biota
|
|
(1)
|
The substance Alachlor has been moved to Part C of Annex II
|
|
(2)
|
Anthracene
|
Industrial substances
|
120‑12‑7
|
204-371-1
|
0,1
|
0,1
|
0,1
|
0,1
|
|
X
|
|
X
|
|
(3)
|
Atrazine
|
Herbicides
|
1912‑24‑9
|
217-617-8
|
0,6
|
0,6
|
2,0
|
2,0
|
|
|
|
|
|
(4)
|
Benzene
|
Industrial substances
|
71‑43‑2
|
200-753-7
|
10
|
8
|
50
|
50
|
|
|
|
|
|
(5)
|
Brominated diphenylethers
|
Industrial substances
|
not applicable
|
not applicable
|
|
|
0,14 (7)
|
0,014 (7)
|
[0,00028] (7)
|
X (8)
|
X
|
X
|
|
(6)
|
Cadmium and its compounds
(depending on water hardness classes) (9)
|
Metals
|
7440‑43‑9
|
231-152-8
|
≤ 0,08 (Class 1)
0,08 (Class 2)
0,09 (Class 3)
0,15 (Class 4)
0,25 (Class 5)
|
0,2
|
≤ 0,45 (Class 1)
0,45 (Class 2)
0,6 (Class 3)
0,9 (Class 4)
1,5 (Class 5)
|
≤ 0,45 (Class 1)
0,45 (Class 2)
0,6 (Class 3)
0,9 (Class 4)
1,5 (Class 5)
|
|
X
|
|
X
|
|
(6a)
|
The substance Carbon tetrachloride has been moved to Part C of Annex II
|
|
(7)
|
C10‑13 Chloroalkanes (10)
|
Industrial substances
|
85535‑84‑8
|
287-476-5
|
0,4
|
0,4
|
1,4
|
1,4
|
|
X
|
|
X
|
|
(8)
|
The substance Chlorfenvinphos has been moved to Part C of Annex II
|
|
(9)
|
Chlorpyrifos (Chlorpyrifos-ethyl)
|
Organophosphate pesticides
|
2921‑88‑2
|
220-864-4
|
4,6 × 10-4
|
4,6 × 10-5
|
0,0026
|
5,2 × 10-4
|
|
X
|
X
|
X
|
(9a)
|
Cyclodiene pesticides:
Aldrin
Dieldrin
Endrin
Isodrin
|
Organochlorine pesticides
|
309‑00‑2
60‑57‑1
72‑20‑8
465‑73‑6
|
206-215-8
200-484-5
200-775-7
207-366-2
|
Σ = 0,01
|
Σ = 0,005
|
not applicable
|
not applicable
|
|
X
|
|
|
|
(9b)
|
DDT total (11)
|
Organochlorine pesticides
|
not applicable
|
not applicable
|
0,025
|
0,025
|
not applicable
|
not applicable
|
|
X
|
|
|
|
|
para-para‑DDT
|
|
50‑29‑3
|
200-024-3
|
0,01
|
0,01
|
not applicable
|
not applicable
|
|
X
|
|
|
|
(10)
|
1,2‑Dichloroethane
|
Industrial substances
|
107‑06‑2
|
203-458-1
|
10
|
10
|
not applicable
|
not applicable
|
|
X
|
|
|
|
(11)
|
Dichloromethane
|
Industrial substances
|
75‑09‑2
|
200-838-9
|
20
|
20
|
not applicable
|
not applicable
|
|
|
|
|
|
(12)
|
Di(2‑ethylhexyl)-phthalate (DEHP)
|
Industrial substances
|
117‑81‑7
|
204-211-0
|
1,3
|
1,3
|
not applicable
|
not applicable
|
|
X
|
|
X
|
|
(13)
|
Diuron
|
Herbicides
|
330‑54‑1
|
206-354-4
|
0,049
|
0,0049
|
0,27
|
0,054
|
|
|
|
|
|
(14)
|
Endosulfan
|
Organochlorine pesticides
|
115‑29‑7
|
204-079-4
|
0,005
|
0,0005
|
0,01
|
0,004
|
|
X
|
|
|
|
(15)
|
Fluoranthene
|
Industrial substances
|
206‑44‑0
|
205-912-4
|
7,62 × 10-4
|
7,62 × 10-4
|
0,12
|
0,012
|
6,1
|
X
|
X
|
X
|
|
(16)
|
Hexachlorobenzene
|
Organochlorine pesticides
|
118‑74‑1
|
204-273-9
|
|
|
0,5
|
0,05
|
20
|
X
|
|
X
|
|
(17)
|
Hexachlorobutadiene
|
Industrial substances (solvents)
|
87‑68‑3
|
201-765-5
|
9 × 10-4
|
|
0,6
|
0,6
|
21
|
X
|
|
X
|
|
(18)
|
Hexachlorocyclohexane
|
Insecticides
|
608‑73‑1
|
210-168-9
|
0,02
|
0,002
|
0,04
|
0,02
|
|
X
|
|
X
|
|
(19)
|
Isoproturon
|
Herbicides
|
34123‑59‑6
|
251-835-4
|
0,3
|
0,3
|
1,0
|
1,0
|
|
|
|
|
|
(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 compounds
|
Metals
|
7439‑97‑6
|
231-106-7
|
|
|
0,07
|
0,07
|
[10] (13)
|
X
|
X
|
X
|
|
(22)
|
Naphthalene
|
Industrial substances
|
91‑20‑3
|
202-049-5
|
2
|
2
|
130
|
130
|
|
|
|
|
|
(23)
|
Nickel and its compounds
|
Metals
|
7440‑02‑0
|
231-111-4
|
2 (12)
|
3,1
|
8,2
|
8,2
|
|
|
|
|
|
(24)
|
Nonylphenols (14)
(4-Nonylphenol)
|
Industrial substances
|
84852-15-3
|
284-325-5
|
0,037
|
0,0018
|
2,1
|
0,17
|
|
X
|
|
|
|
(25)
|
Octylphenols (15)
((4-(1,1',3,3'-tetramethylbutyl)-phenol))
|
Industrial substances
|
140‑66‑9
|
205-426-2
|
0,1
|
0,01
|
not applicable
|
not applicable
|
|
X
|
|
|
|
(26)
|
Pentachlorobenzene
|
Industrial substances
|
608‑93‑5
|
210-172-0
|
0,007
|
0,0007
|
not applicable
|
not applicable
|
|
X
|
|
X
|
|
(27)
|
Pentachlorophenol
|
Organochlorine pesticides
|
87‑86‑5
|
201-778-6
|
0,4
|
0,4
|
1
|
1
|
|
X
|
|
|
|
(28)
|
Polyaromatic hydrocarbons (PAHs) (16)
|
Combustion products
|
not applicable
|
not applicable
|
not applicable
|
not applicable
|
not applicable
|
not applicable
|
Sum of Benzo(a)pyrene equivalents [0.6](17)
|
X
|
X
|
X
|
|
|
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 applicable
|
not applicable
|
see footnote 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 substances
|
127‑18‑4
|
204-825-9
|
10
|
10
|
not applicable
|
not applicable
|
|
|
|
|
|
(29b)
|
Trichloroethylene
|
Industrial substances
|
79‑01‑6
|
201-167-4
|
10
|
10
|
not applicable
|
not applicable
|
|
X
|
|
|
|
(30)
|
Tributyltin compounds (18) (Tributyltin-cation)
|
Biocides
|
36643-28-4
|
not applicable
|
0,0002
|
0,0002
|
0,0015
|
0,0015
|
[1,3] (19)
|
X
|
X
|
X
|
|
(31)
|
Trichlorobenzenes
|
Industrial substances (solvents)
|
12002-48-1
|
234-413-4
|
0,4
|
0,4
|
not applicable
|
not applicable
|
|
|
|
|
|
(32)
|
Trichloromethane
|
Industrial substances
|
67-66-3
|
200-663-8
|
2,5
|
2,5
|
not applicable
|
not applicable
|
|
|
|
|
|
(33)
|
Trifluralin
|
Herbicides
|
1582-09-8
|
216-428-8
|
0,03
|
0,03
|
not applicable
|
not applicable
|
|
X
|
|
|
|
(34)
|
Dicofol
|
Organochlorine pesticides
|
115-32-2
|
204-082-0
|
[4,45 × 10-3]
|
[0,185 × 10-3]
|
not applicable (20)
|
not applicable (20)
|
[5.45]
|
X
|
|
X
|
|
(35)
|
Perfluorooctane sulfonic acid and its derivatives (PFOS)
|
Industrial substances
|
1763-23-1
|
217-179-8
|
Coverd by substance group 65 (Per- and poly-fluorinated alkyl substances (PFAS) – sum of 24)
|
|
(36)
|
Quinoxyfen
|
Plant protection products
|
124495-18-7
|
not applicable
|
0,15
|
0,015
|
2,7
|
0,54
|
|
X
|
|
X
|
|
(37)
|
Dioxins and dioxin-like compounds (21)
|
Industrial byproducts
|
not applicable
|
not applicable
|
|
|
not applicable
|
not applicable
|
Sum of PCDDs+ PCDFs+ PCB-DLs
equivalents [3,5 10-5] (22)
|
X
|
X
|
X
|
|
(38)
|
Aclonifen
|
Herbicides
|
74070-46-5
|
277-704-1
|
0,12
|
0,012
|
0,12
|
0,012
|
|
|
|
|
|
(39)
|
Bifenox
|
Herbicides
|
42576-02-3
|
255-894-7
|
0,012
|
0,0012
|
0,04
|
0,004
|
|
|
|
|
|
(40)
|
Cybutryne
|
Biocides
|
28159-98-0
|
248-872-3
|
0,0025
|
0,0025
|
0,016
|
0,016
|
|
|
|
|
|
(41)
|
Cypermethrin (23)
|
Pyrethroid pesticides
|
52315-07-8
|
257-842-9
|
3 × 10-5
|
3 × 10-6
|
6 × 10-4
|
6 × 10-5
|
|
|
|
X
|
|
(42)
|
Dichlorvos
|
Organophosphate pesticides
|
62-73-7
|
200-547-7
|
6 × 10-4
|
6 × 10-5
|
7 × 10-4
|
7 × 10-5
|
|
|
|
|
|
(43)
|
Hexabromocyclododecane (HBCDD) (24)
|
Industrial substances
|
See footnote 24
|
See footnote 24
|
[4,6 × 10-4]
|
[2 × 10-5]
|
0,5
|
0,05
|
[3,5]
|
X
|
X
|
X
|
|
(44)
|
Heptachlor and heptachlor epoxide
|
Organochlorine pesticides
|
76-44-8 / 1024-57-3
|
200-962-3/ 213-831-0
|
[1,7 × 10-7]
|
[1,7 × 10-7]
|
3 × 10-4
|
3 × 10-5
|
[0,013]
|
X
|
X
|
X
|
|
(45)
|
Terbutryn
|
Herbicides
|
886-50-0
|
212-950-5
|
0,065
|
0,0065
|
0,34
|
0,034
|
|
|
|
|
|
(46)
|
17 alpha-ethinylestradiol (EE2)
|
Pharmaceuticals (Estrogenic hormones)
|
57-63-6
|
200-342-2
|
1,7 × 10-5
|
1,6 × 10-6
|
not derived
|
not derived
|
|
|
|
|
|
(47)
|
17 beta-estradiol (E2)
|
Pharmaceuticals (Estrogenic hormones)
|
50-28-2
|
200-023-8
|
0,00018
|
9 × 10-6
|
not derived
|
not derived
|
|
|
|
|
|
(48)
|
Acetamiprid
|
Neonicotinoid pesticides
|
135410-20-7 / 160430-64-8
|
603-921-1
|
0,037
|
0,0037
|
0,16
|
0,016
|
|
|
|
|
|
(49)
|
Azithromycin
|
Pharmaceuticals (Macrolide antibiotics)
|
83905-01-5
|
617-500-5
|
0,019
|
0,0019
|
0,18
|
0,018
|
|
|
|
X
|
|
(50)
|
Bifenthrin
|
Pyrethroid pesticides
|
82657-04-3
|
617-373-6
|
9,5 × 10-5
|
9,5 × 10-6
|
0,011
|
0,001
|
|
|
|
X
|
|
(51)
|
Bisphenol-A (BPA)
|
Industrial substances
|
80-05-7
|
201-245-8
|
3,4 × 10-5
|
3,4 × 10-5
|
130
|
51
|
0,005
|
X
|
|
|
|
(52)
|
Carbamazepine
|
Pharmaceuticals
|
298-46-4
|
206-062-7
|
2,5
|
0,25
|
1,6 × 103
|
160
|
|
|
|
|
|
(53)
|
Clarithromycin
|
Pharmaceuticals (Macrolide antibiotics)
|
81103-11-9
|
658-034-2
|
0,13
|
0,013
|
0,13
|
0,013
|
|
|
|
X
|
|
(54)
|
Clothianidin
|
Neonicotinoid pesticides
|
210880-92-5
|
433-460-1
|
0,01
|
0,001
|
0,34
|
0,034
|
|
|
|
|
|
(55)
|
Deltamethrin
|
Pyrethroid pesticides
|
52918-63-5
|
258-256-6
|
1,7 × 10-6
|
1,7 × 10-7
|
1,7 × 10-5
|
3,4 × 10-6
|
|
|
|
X
|
|
(56)
|
Diclofenac
|
Pharmaceuticals
|
15307-86-5 / 15307-79-6
|
239-348-5 / 239-346-4
|
0,04
|
0,004
|
250
|
25
|
|
|
|
X
|
|
(57)
|
Erythromycin
|
Pharmaceuticals (Macrolide antibiotics)
|
114-07-8
|
204-040-1
|
0,5
|
0,05
|
1
|
0,1
|
|
|
|
X
|
|
(58)
|
Esfenvalerate
|
Pyrethroid pesticides
|
66230-04-4
|
613-911-9
|
1,7 × 10-5
|
1,7 × 10-6
|
0,0085
|
0,00085
|
|
|
|
X
|
|
(59)
|
Estrone (E1)
|
Pharmaceuticals (Estrogenic hormones)
|
53-16-7
|
200-164-5
|
3,6 × 10-4
|
1,8 × 10-5
|
not derived
|
not derived
|
|
|
|
|
|
(60)
|
Glyphosate
|
Herbicides
|
1071-83-6
|
213-997-4
|
0,1 (25)
86,7 (26)
|
8,67
|
398,6
|
39,86
|
|
|
|
|
|
(61)
|
Ibuprofen
|
Pharmaceuticals
|
15687-27-1
|
239-784-6
|
0,22
|
0,022
|
|
|
|
|
|
X
|
|
(62)
|
Imidacloprid
|
Neonicotinoid pesticides
|
138261-41-3 / 105827-78-9
|
428-040-8
|
0,0068
|
6,8 × 10-4
|
0,057
|
0,0057
|
|
|
|
|
|
(63)
|
Nicosulfuron
|
Herbicides
|
111991-09-4
|
601-148-4
|
0,0087
|
8,7 × 10-4
|
0,23
|
0,023
|
|
|
|
|
|
(64)
|
Permethrin
|
Pyrethroid pesticides
|
52645-53-1
|
258-067-9
|
2,7× 10-4
|
2.7 × 10-5
|
0,0025
|
2,5 × 10-4
|
|
|
|
X
|
|
(65)
|
Per- and poly-fluorinated alkyl substances (PFAS) – sum of 24 (27)
|
Industrial substances
|
not applicable
|
not applicable
|
Sum of PFOA equivalents 0,0044 (28)
|
Sum of PFOA equivalents 0,0044 (28)
|
not applicable
|
not applicable
|
Sum of PFOA equivalents 0,077 (28)
|
X
|
X
|
X
|
|
(66)
|
Silver
|
Metals
|
7440-22-4
|
231-131-3
|
0,01
|
0,006 (10% salinity)
0,17 (30% salinity)
|
0,022
|
not derived
|
|
|
|
|
|
(67)
|
Thiacloprid
|
Neonicotinoid pesticides
|
111988-49-9
|
601-147-9
|
0,01
|
0,001
|
0,05
|
0,005
|
|
|
|
|
|
(68)
|
Thiamethoxam
|
Neonicotinoid pesticides
|
153719-23-4
|
428-650-4
|
0,04
|
0,004
|
0,77
|
0,077
|
|
|
|
|
|
(69)
|
Triclosan
|
Biocides
|
3380-34-5
|
222-182-2
|
0,02
|
0,002
|
0,02
|
0,002
|
|
|
|
|
|
(70)
|
Total of active substances in pesticides, including their relevant metabolites, degradation and reaction products (29)
|
Plant protection products and biocides
|
|
|
0,5 (30)
|
0,5 (30)
|
|
|
|
|
|
|
(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
Part 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
|
[Entry] N°
|
Name of substance
|
Category of substances
|
CAS number (1)
|
EU number (2)
|
AA‑EQS (3)
Inland surface waters (4)
[µg/l]
|
AA‑EQS (3)
Other surface waters
[µg/l]
|
MAC‑EQS (5)
Inland surface waters(4)
[µg/l]
|
MAC‑EQS (5)
Other surface waters
[µg/l]
|
EQS
Biota (6
[µg/kg wet weight] or EQS Sediment where 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)
|
Pesticide
|
470-90-6
|
207-432-0
|
0,1
|
0,1
|
0,3
|
0,3
|
|
|
|
4
|
Simazine (7)
|
Pesticide
|
122-34-9
|
204-535-2
|
1
|
1
|
4
|
4
|
|
|