S.I. No. 99/2023 - European Union (Drinking Water) Regulations 2023

Type Statutory Instrument
Publication 2023-03-10
Last updated 2026-01-02
State In force superseded text
Text As published
articles 35

This is the act as published. Later amendments are not folded into the text below: each one is a separate act in this repository and an entry in this law's history.

2 amending acts · 2026-01-02, S.I. No. 673/2025 - European Union (Drinking Water) (Amendment) Regulations 2025

Reform history JSON API

commits an offence.

Derogations

18.

18.

(1) In duly justified circumstances, a departure from the parametric values set out in Table B in Schedule 1, or set in accordance with Regulation 6, up to a maximum value for each such departure to be determined by the EPA, may on application by Uisce Éireann in respect of a public water supply, or by the relevant local authority in respect of a private water supply, subject to the agreement of the HSE, be granted by the EPA in relation to a water supply, provided no such departure constitutes a potential danger to human health and that the supply of water intended for human consumption in the area concerned cannot otherwise be maintained by any other reasonable means; such derogations shall be limited to the following:

PART 5 MINIMUM REQUIREMENTS

Minimum hygiene requirements for materials that come into contact with water intended for human consumption

19.

19.

(1) For the purposes of Regulation 4, a water supplier shall ensure that materials that are intended to be used in their new installations or, in the case of repair works or reconstruction, in existing installations for the abstraction, treatment, storage or distribution of water intended for human consumption and that come into contact with such water do not—

Minimum requirement for treatment chemicals and filter media that come into contact with water intended for human consumption

20.

20.

(1) For the purposes of Regulation 4, a water supplier shall ensure that treatment chemicals and filter media that come into contact with water intended for human consumption do not—

Access to water intended for human consumption

21.

21.

(1) A water supplier, without prejudice to the principles of subsidiarity and proportionality, whilst taking into account the local, regional and cultural perspectives and circumstances for water distribution, shall take the necessary measures to improve or maintain access to water intended for human consumption for all its customers, in particular for those in vulnerable or marginalised groups.

PART 6 AUTHORISED OFFICERS

Authorised officers

22.

22.

(1) A supervisory authority, may appoint in writing such and so many persons, including members of the staff of the supervisory authority concerned, to be authorised officers for the purpose of obtaining, or verifying, any information which may be required in relation to a matter mentioned in these Regulations, and such appointment may be specified to be for a fixed period.

commits an offence.

Powers of authorised officers

23.

23.

(1) For the purpose of obtaining, or verifying, any information which may be required in relation to a matter mentioned in these Regulations, an authorised officer may, on production of an appointment under Regulation 22 authorising him or her to exercise one or more specified powers under paragraph (2), exercise that power or those powers.

“records” includes, in addition to records in writing—

and a reference to a copy of records includes, in the case of records falling within paragraph (a) only, a transcript of the sounds or signals embodied therein, in the case of records falling within paragraph (b), a still reproduction of the images embodied therein and, in the case of records falling within both of those paragraphs, such a transcript and such a still reproduction;

“tape” includes—

PART 7 PENALTIES AND PROSECUTIONS

Penalties and prosecutions

24.

24.

(1) A person that commits an offence under Regulation 4(7), 4(8), 5(4), 11(7), 13(19), 14(8), 15(6), 17(14), 22(6), 25(1), 25(2), 25(3) or 27(2) is liable—

Offences in relation to water

25.

25.

(1) A person that causes—

of a source of a water supply that is intended for human consumption causing the supply of water that is not wholesome or clean or causes a risk to human health, commits an offence.

commits an offence.

Offences by bodies corporate

26.

26.

(1) Where an offence under these Regulations has been committed by a body corporate and is proved to have been committed with the consent or connivance of or to be attributable to any neglect on the part of a person being a director, manager, secretary or other similar officer of the body corporate, or of a person who was purporting to act in any such capacity, that person as well as the body corporate is guilty of an offence and is liable to be proceeded against and punished as if that person was guilty of the first-mentioned offence.

PART 8 SUPERVISORY AUTHORITIES

Directions of supervisory authorities

27.

27.

(1) A supervisory authority may give such directions as it considers appropriate for the purposes of its functions under these Regulations.

Guidelines: practical guidance for water suppliers and supervisory authorities

28.

28.

(1) The EPA shall issue guidelines for the purposes of providing practical guidance–

Charges by supervisory authorities

29.

29.

(1) A supervisory authority may charge for monitoring the quality of water supplies intended for human consumption.

Intervention, and performance verification, by supervisory authority

30.

30.

(1) Without prejudice to Regulation 15, having exercised such of its powers under these Regulations as it considers appropriate, and having considered any information furnished to it or otherwise coming into its possession in consequence of that exercise, each supervisory authority shall, with a view to achieving satisfactory compliance of water supplied for human consumption with relevant water quality standards or other parametric values specified in Schedule 1, do one, or both, of the following:

Injunctive relief

31.

31.

(1) Where, on application by a supervisory authority to the High Court, the court is satisfied that a person has failed to comply with a direction or a requirement of, or under, these Regulations, the court may by order—

PART 9 FINAL PROVISIONS

Service of directions

32.

32.

(1) Where a direction is required to be issued to a person under these Regulations, it shall be in writing addressed to the party concerned and given to the party in one of the following ways:

and it is also given in one of the other ways mentioned in subparagraphs (a) to (d).

Information Sharing

33.

33.

The supervisory authorities, the source protection authorities and the water suppliers shall share such information appropriate to their functions, as may be required and requested, in writing, under these Regulations.

Transitional provisions

34.

34.

(1) The parametric values set under Regulation 6 in respect of Bisphenol A, Chlorate, Chlorite, Haloacetic Acids, Microcystin-LR, PFAS Total, Sum of PFAS and Uranium shall not apply in respect of water intended for human consumption up to, and including, 11 January 2026.

Revocations

35.

35.

(1) Subject to paragraph (2), the following are revoked:

SCHEDULE 1

Regulations 4(2), 6(1) to (4), 7, 8(2), 10(4), 11(5), 12(1), (3) and (4), 13(2), (3) (5) and (11) to (13), 14(2), 15(3), 16(1), 17(1) to (5), (8), (10) and (13), 18(1) and 30(1)

MINIMUM REQUIREMENTS FOR PARAMETRIC VALUES USED TO ASSESS THE QUALITY OF WATER INTENDED FOR HUMAN CONSUMPTION

TABLE A

MICROBIOLOGICAL PARAMETERS

Parameter Parametric value Unit Notes
Intestinal enterococci 0 number/100 ml Note 1
Escherichia coli (E.coli) 0 number/100 ml Note 1

Note to Table

Note 1: For water put into bottles or containers, the unit is number/250 ml.

TABLE B

CHEMICAL PARAMETERS

Parameter Parametric value Unit Notes
Acrylamide 0.10 μg/l Note 1
Antimony 10 μg/l
Arsenic 10 μg/l
Benzene 1.0 μg/l
Benzo(a)pyrene 0.010 μg/l
Bisphenol A 2.5 μg/l
Boron 1.5 mg/l Note 2
Bromate 10 μg/l
Cadmium 5.0 μg/l
Chlorate 0.25 mg/l Note 3
Chlorite 0.25 mg/l Note 4
Chromium 25 μg/l Note 5
Copper 2.0 mg/l
Cyanide 50 μg/l
1,2-dichloroethane 3.0 μg/l
Epichlorohydrin 0.10 μg/l Note 6
Fluoride 1.5 mg/l
Haloacetic acids (HAAs) 60 μg/l Note 7
Lead 5 μg/l Notes 8 & 9
Mercury 1.0 μg/l
Microcystin-LR 1.0 μg/l Note 10
Nickel 20 μg/l
Nitrate 50 mg/l Note 11
Nitrite 0.50 mg/l Note 11
Pesticides 0.10 μg/l Notes 12, 13 & 14
Pesticides — Total 0.50 μg/l Note 15
PFAS Total 0.50 μg/l Note 16
Sum of PFAS 0.10 μg/l Note 17
Polycyclic aromatic hydrocarbons 0.10 μg/l Note 18
Selenium 20 μg/l Note 19
Tetrachloroethene and Trichloroethene 10 μg/l Note 20
Trihalomethanes Total 100 μg/l Note 21
Uranium 30 μg/l
Vinyl chloride 0.50 μg/l Note 22

Notes to Table

Note 1 The parametric value of 0.10 μg/l refers to the residual monomer concentration in the water as calculated according to specifications of the maximum release from the corresponding polymer in contact with the water;

Note 2 A parametric value of 2.4 mg/l shall be applied when desalinated water is the predominant water source of the supply system concerned or in regions where geological conditions could lead to high levels of boron in groundwater;

Note 3 A parametric value of 0.70 mg/l shall be applied where a disinfection method that generates chlorate, in particular chlorine dioxide, is used for disinfection of water intended for human consumption. Where possible, without compromising disinfection, the water supplier shall strive for a lower value. This parameter shall be measured only if such disinfection methods are used;

Note 4 A parametric value of 0.70 mg/l shall be applied where a disinfection method that generates chlorite, in particular chlorine dioxide, is used for disinfection of water intended for human consumption. Where possible, without compromising disinfection, the water supplier shall strive for a lower value. This parameter shall be measured only if such disinfection methods are used;

Note 5 A parametric value of 25 μg/l shall be met, at the latest, by 12 January 2036. The parametric value for chromium until that date shall be 50 μg/l;

Note 6 The parametric value of 0.10 μg/l refers to the residual monomer concentration in the water as calculated according to specifications of the maximum release from the corresponding polymer in contact with the water;

Note 7 This parameter shall be measured only when disinfection methods that can generate HAAs are used for the disinfection of water intended for human consumption. It is the sum of the following five representative substances: monochloro-, dichloro-, and trichloro-acetic acid, and mono- and dibromo-acetic acid;

Note 8 The parametric value of 5 μg/l shall be met, at the latest, by 12 January 2036. The parametric value for lead until that date shall be 10 μg/l;

Note 9 After that date, the parametric value of 5μg/l shall be met at least at the point of supply to the domestic distribution system. For the purposes of point (b) of the first subparagraph of Article 11(2) of the Directive, the parametric value of 5 μg/l at the tap shall apply;

Note 10 This parameter shall be measured only in the event of potential blooms in source water (increasing cyanobacterial cell density or bloom forming potential);

Note 11 A water supplier shall ensure that the condition [nitrate]/50 + [nitrite]/3 < 1, where the square brackets signify the concentrations in mg/l for nitrate (NO3) and nitrite (NO2), is complied with and that the parametric value of 0.10 mg/l for nitrites is complied with ex water treatment works;

Note 12 ‘Pesticides’ means the following:

and their metabolites as defined in point (32) of Article 3 of Regulation (EC) No 1107/2009 of the European Parliament and of the Council of 21 October 2009,8 that are considered relevant for water intended for human consumption. A pesticide metabolite shall be deemed relevant for water intended for human consumption if there is a reason to consider that it has intrinsic properties comparable to those of the parent substance in terms of its pesticide target activity or that either itself or its transformation products generate a health risk for consumers.

Note 13 The parametric value of 0.10 μg/l shall apply to each individual pesticide. In the case of aldrin, dieldrin, heptachlor and heptachlor epoxide, the parametric value shall be 0.030 μg/l;

Note 14 The Minister for Agriculture, Food and the Marine shall define a guidance value to manage the presence of non-relevant metabolites of pesticides in water intended for human consumption. Only pesticides which are likely to be present in a given supply need to be monitored. Based on the data reported by the EPA, the European Commission may establish a database of pesticides and their relevant metabolites taking into account their possible presence in water intended for human consumption;

Note 15 ‘Pesticides Total’ means the sum of all individual pesticides, as defined in the previous row, detected and quantified in the monitoring procedure;

Note 16 ‘PFAS Total’ means the totality of per- and polyfluoroalkyl substances. This parametric value shall only apply once technical guidelines for monitoring this parameter are developed by the European Commission in accordance with Article 13(7) of the Directive. The EPA may then decide to use either one or both of the parameters ‘PFAS Total’ or ‘Sum of PFAS’;

Note 17 ‘Sum of PFAS’ means the sum of per-and polyfluoroalkyl substances considered a concern as regards water intended for human consumption listed in point 3 of Part 2 of Schedule 3. This is a subset of ‘PFAS Total’ substances that contain a perfluoroalkyl moiety with three or more carbons (i.e. –CnF2n-, n > 3) or a perfluoroalky-lether moiety with two or more carbons (i.e. –CnF2nOCmF2m-, n and m > 1);

Note 18 Sum of concentrations of the following specified compounds: benzo(b)fluor-anthene, benzo(k)fluoranthene, benzo(ghi)perylene, and indeno(1,2,3-cd)pyr-ene;

Note 19 A parametric value of 30 μg/l shall be applied for regions where geological conditions could lead to high levels of selenium in groundwater;

Note 20 The sum of concentrations of these two parameters;

Note 21 Where possible, without compromising disinfection, water suppliers shall strive for a lower parametric value. It is the sum of concentrations of the following specified compounds: chloroform, bromoform, dibromochloromethane and bromodichloromethane;

Note 22 The parametric value of 0.50 μg/l refers to the residual monomer concentrations in the water as calculated according to specifications of the maximum release from the corresponding polymer in contact with the water;

TABLE C

INDICATOR PARAMETERS

Parameter Parametric value Unit Notes
Aluminium 200 μg/l
Ammonium 0.50 mg/l
Chloride 250 mg/l Note 1
Clostridium perfringens (including spores) 0 number/100 ml Note 2
Colour Acceptable to consumers and no abnormal change
Conductivity 2,500 μS cm^-1 at 20 °C Note 3
Hydrogen ion concentration ≥ 6.5 and ≤9.5 pH units Note 3 & 4
Iron 200 μg/l
Manganese 50 μg/l
Odour Acceptable to consumers and no abnormal change
Oxidisability 5.0 mg/l O2 Note 5
Sulphate 250 mg/l Note 1
Sodium 200 mg/l
Taste Acceptable to consumers and no abnormal change
Colony count 22 °C No abnormal change
Coliform bacteria 0 number/100 ml Note 6
Total organic carbon (TOC) No abnormal change Note 7
Turbidity Acceptable to consumers and no abnormal change

Water should not be aggressive or corrosive. This applies particularly to water undergoing treatment (demineralization, softening, membrane treatment, reverse osmosis, etc.).

Where water intended for human consumption is derived from treatment that significantly demineralizes or softens water, calcium and magnesium salts could be added to condition the water in order to reduce any possible negative health impact, as well as to reduce the corrosiveness or aggressivity of water and to improve taste. Minimum concentrations of calcium and magnesium or total dissolved solids in softened or demineralized water could be established taking into account the characteristics of water that enters those processes.

Notes to Table

Note 1: The water should not be corrosive;

Note 2: The parameter shall be measured if the risk assessment indicates that it is appropriate to do so;

Note 3: The water should not be aggressive;

Note 4: For still water put into bottles or containers, the minimum value may be reduced to 4,5 pH units. For water put into bottles or containers which is naturally rich in or artificially enriched with carbon dioxide, the minimum value may be lower.

Note 5: This parameter need not be measured if the parameter TOC is analysed;

Note 6: For water put into bottles or containers, the unit is number / 250 ml;

Note 7: This parameter need not be measured for supplies of less than 10,000 cubic metres a day.

TABLE D

PARAMETERS RELEVANT FOR THE RISK ASSESSMENT OF DOMESTIC DISTRIBUTION SYSTEMS

Parameter Parametric value Unit Notes
Legionella < 1000 CFU/1 This parametric value is set for the purposes of Regulations 12 and 17. Actions provided for in those Regulations could be considered even when the value is below the parametric value, e.g. in cases of infections and outbreaks. In such cases, the source of infection should be confirmed and the species of Legionella should be identified.
Lead 10 μg/l This parametric value is set for the purposes of Regulations 12 and 17. Water suppliers should use their best endeavours to achieve the lower value of 5 μg/l by 12 January 2036.

SCHEDULE 2 Regulations 10(10) and (13), 11(4) and 13(5), (6), (13) and (17)

MONITORING

PART 1 General objectives and monitoring programmes for water intended for human consumption

1.

Monitoring programmes established pursuant to Regulation 13(13) for water intended for human consumption shall—

2.

Monitoring programmes established pursuant to Regulation 13(13) shall include one or a combination of the following:

In addition, monitoring programmes may consist of the following

3.

Monitoring programmes shall also include an operational monitoring programme that provides rapid insight into operational performance and water quality problems and that allows rapid pre-planned remedial action. Such operational monitoring programmes shall be supply-specific, taking into account the outcomes of the identification of hazards and hazardous events and risk assessment of the supply system, and shall be intended to confirm the effectiveness of all control measures in abstraction, treatment, distribution and storage.

The operational monitoring programme shall include the monitoring of the parameter ‘turbidity’ at the water supply plant’ in order to regularly control the efficacy of physical removal by filtration processes, in accordance with the reference values and frequencies indicated in the following table (not applicable for groundwater sources where turbidity is caused by iron and manganese):

TABLE

Operational parameter Reference value
turbidity at the water supply plant 0.3 NTU in 95 % of samples and none to exceed 1 NTU
Volume (m3) of water distributed or produced each day within a supply zone Minimum frequency of sampling and analysis
≤ 1,000 Weekly
> 1,000 to ≤ 10,000 Daily
> 10,000 Continuous

The operational monitoring programme shall also include the monitoring of the following parameters in raw water to control the efficacy of the treatment processes against microbiological risks:

Operational parameter Reference value Unit Notes
Somatic coliphages 50 (for raw water) Plaque Forming Units (PFU)/100ml This parameter shall be measured if the risk assessment indicates that it is appropriate to do so. If it is found in raw water at concentrations > 50 PFU/100 ml, it should be analysed after steps of the treatment train in order to determine log removal by the barriers in the place and to assess whether the risk of a breakthrough of pathogenic viruses is sufficiently under control.
4.

The EPA shall ensure that monitoring programmes are reviewed on a continuous basis and updated or confirmed not less than once every 6 years.

PART 2 Parameters and sampling frequencies

Point 1 - List of parameters

Group A:

The following parameters (Group A) shall be monitored in accordance with the monitoring frequencies set out in Table of point 2:

Under specific circumstances, the following parameters shall be added to the Group A parameters:

Escherichia coli (E.coli) and intestinal enterococci are considered ‘core parameters’ and their monitoring frequencies shall not be the subject of a reduction due to a risk assessment of the supply system in accordance with Regulation 11 and Part 3 of this schedule. They shall always be monitored not less than at the frequencies set out in the Table in point 2.

Group B:

In order to determine compliance with all parametric values set out in these Regulations, all other parameters not analysed under Group A and set in accordance with Regulation 6, except for parameters set out in Table D in Schedule 1, shall be monitored not less than at the frequencies set out in Note 2 to the Table, unless a different sampling frequency is determined on the basis of a risk assessment of the supply system carried out in accordance with Regulation 11 and Part 3 of this schedule.

Point 2 - Sampling frequencies

TABLE

Minimum frequency of sampling and analysis for compliance monitoring

Volume of water distributed or produced each day within a supply zone (Notes 1 and 2) m3 Volume of water distributed or produced each day within a supply zone (Notes 1 and 2) m3 Group A parameter number of samples per year Group B parameter number of samples per year
< 10 > 0 (Note 4) > 0 (Note 4)
≥ 10 ≤ 100 2 1 (Note 5)
> 100 ≤ 1,000 4 1
> 1,000 ≤ 10,000 4 for the first 1,000 m3/d + 3 for each additional 1,000 m3/d and part thereof of the total volume (Note 3) 1 for the first 1,000 m3/d + 1 for each additional 4,500 m3/d and part thereof of the total volume (Note 3)
> 10,000 ≤ 100,000 4 for the first 1,000 m3/d + 3 for each additional 1,000 m3/d and part thereof of the total volume (Note 3) 3 for first 10,000 m3/d + 1 for each additional 10,000 m3/d and part thereof of the total volume (Note 3)
> 100,000 4 for the first 1,000 m3/d + 3 for each additional 1,000 m3/d and part thereof of the total volume (Note 3) 12 for first 100,000 m3/d +1 for each additional 25,000 m3/d and part thereof of the total volume (Note 3)

Notes to Table

Note 1: A supply zone is geographically defined area within which water intended for human consumption comes from one or more sources and within which the water quality can be considered as being approximately uniform;

Note 2: The volumes are calculated as averages taken over a calendar year. The number of inhabitants in a supply zone may be used instead of the volume of water to determine the minimum frequency, assuming water consumption of 200 l/ (day*capita);

Note 3: The frequency indicated is calculated as follows: e.g. 4,300 m3/d = 16 samples for Group A parameters (four of the first 1,000 m3/d + 12 for additional 3,300 m3/d);

Note 4: For water suppliers, where an exemption has not been granted under Regulation 3(2), the EPA shall lay down the minimum sampling frequency for parameters of Group A and B, provided that core parameters are monitored not less than once per year;

Note 5: The EPA may reduce the sampling frequency, provided that all parameters set in accordance with Regulation 6 are monitored not less than once every six years and are monitored in cases where a new water source is integrated into the water supply system or changes to that system, as a result of which a potentially adverse effect on the quality of water is to be expected, are made;

PART 3 Risk assessment and risk management of the supply system

1.

Based on the outcome of risk assessment of the supply system as referred to in Regulation 11, the list of parameters considered in the monitoring shall be extended and the sampling frequencies set out in Part 2 increased where any of the following conditions is fulfilled:

2.

As a result of a risk assessment of the supply system, the list of parameters considered in the monitoring and the sampling frequencies set out in Part 2 may be reduced provided that the following conditions are met:

Where monitoring results, demonstrating that the conditions set out in points (2)(b) to (2)(e) are met, are already available by 12 January 2021, those monitoring results may, from that date, be used to adapt the monitoring following the risk assessment of the supply system.

Where adjustments of monitoring have already been implemented following risk assessment of the supply system in accordance, inter alia, with Part C of Annex II of Council Directive 98/83/EC of 3 November 19989 , the EPA may provide for the possibility to confirm their validity without requiring monitoring in accordance with point 2(b) and 2(c) over a further period of not less than three years from points representative of the whole supply zone.

PART 4 Sampling methods and sampling points

1.

Sampling points shall be determined so as to ensure compliance with Regulation 7(1). In the case of a distribution network, the water supplier may take samples within the supply zone or at the treatment works for particular parameters if it can be demonstrated that there would be no adverse change to the measured value of the parameters concerned. As far as possible, the number of samples shall be distributed equally in time and location.

2.

Sampling at the point of compliance shall meet the following requirements:

3.

Samples for Legionella in domestic distribution systems shall be taken at risk points for proliferation of Legionella, points representative for systemic exposure to Legionella, or both. The supervisory authority shall establish guidelines for sampling methods for Legionella.

4.

Sampling in the distribution network, with the exception of sampling at the consumers’ tap shall be in accordance with ISO 5667-5. For microbiological parameters, samples in the distribution network shall be taken and handled in accordance with I.S. EN ISO 19458, sampling purpose A.

SCHEDULE 3

Regulation 13(9)

SPECIFICATIONS FOR THE ANALYSIS OF PARAMETERS

Water suppliers shall ensure that the methods of analysis used for the purposes of monitoring and demonstrating compliance with these Regulations, with the exception of turbidity, are validated and documented in accordance with I.S. EN ISO/IEC 17025 or other equivalent standards accepted at international level. Water suppliers shall ensure that laboratories or parties contracted by laboratories apply quality management system practices in accordance with I.S. EN ISO/IEC 17025 or other equivalent standards accepted at international level.

For the purposes of assessing the equivalence of alternative methods with the methods laid down in this Schedule, the laboratories, or parties contracted by laboratories, may use standard I.S. EN ISO 17994, established as the standard on the equivalence of microbiological methods, or standard I.S. EN ISO 16140 or any other similar internationally accepted protocols, to establish the equivalence of methods based on principles other than culturing, which are beyond the scope of I.S. EN ISO 17994.

In the absence of an analytical method meeting the minimum performance criteria set out in Part 2, the water supplier concerned shall ensure that monitoring is carried out using the best available techniques not entailing excessive costs.

PART 1 Microbiological parameters for which methods of analysis are specified

The methods of analysis for microbiological parameters are:

for risk-based verification monitoring and to complement culture methods, in addition methods, such as ISO/TS 12869, rapid culture methods, non –culture-based methods, and molecular-based methods, in particular qPCR, can be used;

for operational monitoring, Part 1 of Schedule 2, I.S. EN ISO 10705-2, and EN ISO 10705-3 can be used.

PART 2 Chemical and indicator parameters for which performance characteristics are specified

1.

Chemical and indicator parameters

For the parameters set out in the Table, the method of analysis used shall, as a minimum, be capable of measuring concentrations equal to the parametric value with a limit of quantification, as defined in point (2) of Article 2 of Commission Directive 2009/90/EC of 31 July 200910 of 30% or less of the relevant parametric value and an uncertainty of measurement as specified in the Table. The result shall be expressed using not less than the same number of significant figures as for the parametric value set out in Tables B and C in Schedule 1.

The uncertainty of measurement laid down in the Table shall not be used as an additional tolerance to the parametric values set out in Schedule 1.

TABLE

Minimum performance characteristic ‘Uncertainty of measurement’

Parameters Uncertainty of measurement (Note 1) % of the parametric value (except for pH) Notes
Aluminium 25
Ammonium 40
Acrylamide 30
Antimony 40
Arsenic 30
Benzo(a)pyrene 50 Note 2
Benzene 40
Bisphenol A 50
Boron 25
Bromate 40
Cadmium 25
Chloride 15
Chlorate 40
Chorite 40
Chromium 30
Copper 25
Cyanide 30 Note 3
1,2-dichloroethane 40
Epichlorohydrin 30
Fluoride 20
HAAs 50
Hydrogen ion concentration pH 0.2 Note 4
Iron 30
Lead 30
Manganese 30
Mercury 30
Microcystin-LR 30
Nickel 25
Nitrate 15
Nitrite 20
Oxidasability 50 Note 5
Pesticides 30 Note 6
PFAS 50
Polycyclic aromatic hydrocarbons 40 Note 7
Selenium 40
Sodium 15
Sulphate 15
Tetrachloroethene 40 Note 8
Trichloroethene 40 Note 8
Trihalomethanes-total 40 Note 7
Total organic carbon (TOC) 30 Note 9
Turbidity 30 Note 10
Uranium 30
Vinyl Chloride 50
2.

Notes to Table

Note 1: Uncertainty of measurement is a non-negative parameter characterising the dispersion of the quantity values being attributed to a measure and, based on the information used. The performance criterion for measurement uncertainty (k = 2) is the percentage of the parametric value stated in the table or any stricter value. The uncertainty of measurement shall be estimated at the level of the parametric value, unless otherwise specified;

Note 2: If the value of uncertainty of measurement cannot be met, the best available technique should be selected (up to 60 %);

Note 3: The method determines total cyanide in all forms;

Note 4: The value of the uncertainty of measurement is expressed in pH units;

Note 5: Reference method: I.S. EN ISO 8467;

Note 6: The performance characteristics for individual pesticides are given as an indication. Values for the uncertainty of measurement as low as 30 % can be achieved for serval pesticides, while higher values up to 80 % may be allowed for a number of pesticides;

Note 7: The performance characteristics apply to individual substances, specified at 25 % of the parametric value set out in Table B in Schedule 1;

Note 8: The performance characteristics apply to individual substances, specified at 50 % of the parametric value set out in Table B in Schedule 1;

Note 9: The uncertainty of measurement should be estimated at the level of 3 mg/l of the total organic carbon (TOC). EN 1484 Guidelines for the determination of TOC and dissolved organic carbon (DOC) shall be used for the specification of the uncertainty of the test method;

Note 10: The uncertainty of measurement should be estimated at the level of 1.0 NTU (nephelometric turbidity units), in accordance with I.S. EN ISO 7027 or another equivalent standard method;

3.

Sum of PFAS

The following substances shall be analysed based on the technical guidelines developed by the European Commission in accordance with Article 13(7) of the Directive:

Those substances shall be monitored when the risk assessment and risk management of the catchment areas for abstraction points carried out in accordance with Regulation 10 conclude that those substances are likely to be present in a given water supply.

SCHEDULE 4

Regulation 14(1) and (3), and 10(4)

INFORMATION TO THE PUBLIC

The information in the following points shall be accessible to consumers on-line, in a user-friendly and customised way, and consumers may obtain access to that information by other means upon justified request:

SCHEDULE 5

Regulation 10(4)

PRINCIPLES FOR SETTING METHODOLOGY

REFERRED TO IN REGULATION 19

Groups of materials

1.

Organic materials

Organic material shall only be made of the following:

Organic materials shall be tested in accordance with Table 1 in line with methods for testing specified in relevant European standards or, in the absence thereof, an internationally or nationally recognised method and shall satisfy the requirements stipulated therein. For this purpose, the test results in terms of substance migration shall be converted into estimated levels at the tap.

2.

Metallic materials

Only metallic materials included in the European positive list of compositions to be established by the European Commission in accordance with point (b) of the first subparagraph of Article 11(2) of the Directive shall be used. The limitations stipulated in the European positive list in respect of the composition of these materials, their use for certain products and the use of these products shall be compiled with.

Metallic materials shall be tested in accordance with the Table in line with methods for testing specified in relevant European standards or, in the absence thereof, an internationally or nationally recognised method and shall satisfy the requirements stipulated therein.

3.

Cementitious materials

Cementitious materials shall only be made of one or more of the following:

Cement-bound materials shall be tested in accordance with the Table in line with methods for testing specified in relevant European standards or, in the absence thereof, an internationally or nationally recognised method and shall satisfy the requirements stipulated therein. For this purpose, the test results in terms of substance migration shall be converted into estimated levels at the tap.

4.

Enamels and ceramic materials

Enamels and ceramic materials shall only be made of starting substances from the European positive list of compositions to be established by the European Commission in accordance with point (b) of the first subparagraph of Article 11(2) of the Directive, after carrying out an assessment of the elements used in the composition of these materials.

Enamels and ceramic materials shall be tested in accordance with the Table in line with methods for testing specified in relevant European standards or, in the absence thereof, an internationally or nationally recognised method and shall satisfy the requirements stipulated therein. For this purpose, the test results in terms of substance migration shall be converted into estimated levels at the tap.

5.

Exceptions for assessment of materials used in minor and assembled components

For assembled products: minor components, parts and materials shall be described in detail and testing shall be reduced accordingly. For this purpose, ‘minor’ refers to a level of influence on the quality of water intended for human consumption that does not require full testing.

TABLE

Testing related to material type

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