The Private Water Supplies (England) (Amendment) Regulations 2018

Type Statutory-Instrument
Publication 2018-06-14
State In force
Department King's Printer of Acts of Parliament
PDF Download
articles Not indexed
Reform history JSON API

Made: 14th June 2018

Laid before Parliament: 18th June 2018

Coming into force: 11th July 2018

The Secretary of State has carried out the public consultation required byArticle 9of Regulation (EC) No. 178/2002 of the European Parliament and of the Council laying down the general principles and requirements of food law, establishing the European Food Safety Authority and laying down procedures in matters of food safety[^f00004].

Citation, commencement and interpretation

1

Amendment of the 2016 Regulations

2

  • E. coli”meansEscherichia coli;

(5) A risk assessment described in paragraph (1) must— (a) satisfy any requirements specified by the Secretary of State in respect of the conduct of such an assessment; (b) satisfy the requirements of European standard EN 15975-2 entitled “Security of Drinking Water Supply - Guidelines for Risk and Crisis Management – Risk Management”[^f00006]; and (c) take into account the results of monitoring conducted under the second paragraph of Article 7(1) and Article 8 of Directive 2000/60/EC of the European Parliament and of the Council establishing a framework for Community action in the field of water policy[^f00007]. (6) A local authority must within 12 months beginning with the day after the day on which it carried out the risk assessment provide the Secretary of State with a summary of the results of that assessment.

(2) A local authority must discharge the obligation described in paragraph (1) by establishing a monitoring programme which consists of either or both of the following— (a) collection and analysis of discrete water samples; (b) measurements recorded by a continuous monitoring process. (3) Monitoring programmes may in addition consist of either or both of the following— (a) inspections of records of the functionality, and maintenance status, of equipment; (b) inspections of the catchment area, water abstraction, treatment, storage and distribution infrastructure.

(10A) The local authority may exclude the indicative dose parameter from monitoring, or reduce the frequency of monitoring in respect of that parameter, for such period as it may decide provided that the parameter is— (a) naturally occurring, and (b) stable.

(4) Compliance samples for chemical parameters including copper, lead and nickel must take the form of a random daytime sample of one litre volume taken at a consumer’s tap without prior flushing. (5) All sampling under this regulation— (a) for chemical parameters in the distribution network must, other than where the sample is taken at a consumer’s tap, be undertaken in accordance with international standard ISO 5667-5 entitled “Water quality. Sampling. Guidance on treatment of drinking water from treatment works and piped distribution systems”[^f00008]; (b) for microbiological parameters in the distribution network and at a consumer’s tap must be undertaken in accordance with European standard EN ISO 19458 entitled “Water Quality – Sampling for microbiological analysis”[^f00009] using sampling procedure A in the distribution network and sampling procedure B at a consumer’s tap.

(6) In any case where the monitoring obligations in respect of a private water supply have been reduced or otherwise varied under Part 2A of Schedule 2 by a local authority and— (a) the local authority considers there to be a significant risk that a private water supply is unwholesome; or (b) the local authority determines as a matter of fact that a private water supply is unwholesome, the reduction or variation in respect of the parameter which has contributed to the risk or fact of unwholesomeness must cease immediately and the standard frequency outlined in Table 2 or Table 3 in Schedule 2 (as applicable) must be reinstated in respect of that parameter.

(d) specify what corrective action must be taken in order to— (i) safeguard human health; (ii) restore the wholesomeness of the water supply; and (iii) maintain the continued wholesomeness of the water supply following its restoration.

(7) Where any relevant person (“P”) who is required by virtue of a notice served under this regulation to take any step in relation to any premises fails to take that step within the period specified in the notice, the local authority which served the notice may take that step itself. (8) Where any step is taken by a local authority in relation to any premises by virtue of paragraph (7), the local authority may recover from P any expenses reasonably incurred by it, or by any person acting on its behalf, in taking that step.

(1) (1) A local authority must monitor for a Group A parameter in accordance with this Part and Part 2A. (2) In this Schedule, “monitoring for a Group A parameter” means sampling for each parameter listed in Column 1 of Table 1 in the circumstances listed in the entry which corresponds with that parameter in Column 2 of Table 1 in order to— (a) determine whether or not the water complies with the concentrations or values in Schedule 1; (b) provide information on the organoleptic and microbiological quality of the water; and (c) establish the effectiveness of the treatment of the water, including disinfection.

Parameter Circumstances
Aluminium Where used as a water treatment chemical or where the water originates from, or is influenced by, surface waters
Ammonium Where chloramination is practised
Coliform bacteria In all supplies
Colony counts 22°C In all supplies
Colour In all supplies
Conductivity In all supplies
E. coli In all supplies
Hydrogen ion In all supplies
Iron Where used as a water treatment chemical or where the water originates from, or is influenced by, surface waters
Manganese Where the water originates from, or is influenced by, surface waters
Nitrate Where chloramination is practised
Nitrite Where chloramination is practised
Odour In all supplies
Taste In all supplies
Turbidity In all supplies

(2) Monitoring for a Group A parameter must be undertaken at the frequencies specified in Table 2.

Volume m³/day Sampling frequency per year
≤ 10 1
> 10 ≤ 100 2
> 100 ≤ 1,000 4
> 1,000 ≤ 2,000 10
> 2,000 ≤ 3,000 13
> 3,000 ≤ 4,000 16
> 4,000 ≤ 5,000 19
> 5,000 ≤ 6,000 22
> 6,000 ≤ 7,000 25
> 7,000 ≤ 8,000 28
> 8,000 ≤ 9,000 31
> 9,000 ≤ 10,000 34
> 10,000 4 + 3 for each 1,000m³/day of the total volume (rounding up to the nearest multiple of 1,000m³/day)

(3) (1) A local authority must monitor for a Group B parameter in accordance with this Part and Part 2A. (2) In this Schedule, “monitoring for a Group B parameter” means sampling for each parameter listed in Parts 1 and 2 of Schedule 1 (other than Group A parameters already being sampled under Part 1 of this Schedule)— (a) in order to provide information necessary to determine whether or not the private water supply satisfies each concentration, value or state prescribed in those Parts of that Schedule; and (b) if disinfection is used, in order to check that disinfection by-products are kept as low as possible without compromising the effectiveness of disinfection. (4) Monitoring for a Group B parameter must be undertaken at the frequencies specified in Table 3.

Volume m³/day Sampling frequency per year
≤ 10 1
> 10 ≤ 3,300 2
> 3,300 ≤ 6,600 3
> 6,600 ≤ 10,000 4
> 10,000 ≤ 100,000 3 + 1 for each 10,000m³/day of the total volume (rounding up to the nearest multiple of 10,000m³/day)
> 100,000 12 + 1 for each 25,000m³/day of the total volume (rounding up to the nearest multiple of 25,000m³/day)

(5) (1) When monitoring for a Group A or Group B parameter, a local authority may reduce the sampling frequency in respect of any parameter in Group A or Group B other than E. coli provided that— (a) the results from samples taken in respect of that parameter collected at regular intervals over a period of at least three years are all at less than 60% of the parametric value; (b) the results of a risk assessment described in regulation 6(l) are considered, and that risk assessment indicates that no factor can be reasonably anticipated to be likely to cause deterioration of the quality of the water; (c) data collected in the course of discharging its monitoring obligations under this Part are taken into account; and (d) at least one sample is taken per year. (2) A local authority may cease to monitor for a Group A or Group B parameter other than E. coli provided that— (a) the results from samples taken in respect of that parameter collected at regular intervals over a period of at least three years are all at less than 30% of the parametric value; (b) the results of a risk assessment described in regulation 6(l) are considered, and that risk assessment indicates that no factor can be reasonably anticipated to be likely to cause deterioration of the quality of the water; and (c) data collected in the course of discharging its monitoring obligations under this Part are taken into account. (3) A local authority may set a higher frequency for any parameter if it considers it appropriate, taking into account the findings of any risk assessment, and may monitor anything else identified in the risk assessment.

(1) (1) A local authority must secure, so far as reasonably practicable, that when it takes, handles, transports, stores or analyses any sample required to be taken for the purposes of this Schedule, or causes any such sample to be taken, handled, transported, stored or analysed, it complies with the appropriate requirements. (2) A local authority must secure that a person accredited by the United Kingdom Accreditation Service[^f00010] checks from time to time the local authority’s compliance with the appropriate requirements. (3) Additionally, when undertaking activity described in sub-paragraph (1) the local authority must demonstrate compliance with the following standards— (a) as regards any such activity, other than analysing samples, on or after 11th July 2020, European standard EN ISO/IEC 17024 entitled “Conformity Assessment. General requirements for bodies operating certification of persons”[^f00011], European standard EN ISO/IEC 17025 entitled “General requirements for the competence of testing and calibration laboratories”[^f00012] or other equivalent standards accepted at international level; (b) as regards the activity of analysing samples, European standard EN ISO/IEC 17025 or another equivalent standard accepted at international level. (4) In this paragraph, “appropriate requirements” means such of the following as are applicable— (a) the sample is representative of the quality of the water at the time of sampling; (b) the person taking the sample is doing so in accordance with a system of quality control to an appropriate standard; (c) the sample is not contaminated in the course of being taken; (d) the sample is kept at such a temperature and in such conditions as will secure that there is no material alteration of the concentration or value for the measurement or observation of which the sample is intended; (e) the sample is analysed whether at the time and place it is taken or as soon as reasonably practicable after it is taken— (i) by or under the supervision of a person who is competent to perform that task, and (i) with the use of such equipment as is suitable for the purpose.

(6) For the parameters set out in Table 3 in Part 2 of this Schedule, the specified performance characteristics are that the method of analysis used must be capable of measuring concentrations equal to the parametric value with a limit of quantification, as defined in Article 2(2) of Commission Directive 2009/90/EC laying down technical specifications for chemical analysis and monitoring of water status[^f00013], of 30% or less of the relevant parametric value and an uncertainty of measurement as specified in that Table. (7) The result must be expressed using at least the same number of significant figures as for the parametric value quoted and in the same units laid down in these Regulations. (8) The uncertainty of measurement laid down in Table 3 in Part 2 of this Schedule must not be used as an additional tolerance to the parametric values set out in Schedule 1.

Parameters Uncertainty of measurement % of the parametric value (except for pH)[^f01000]
(1) “Uncertainty of measurement” is a non-negative parameter characterising the dispersion of the quantity values being attributed to a measurement, 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 better. Measurement uncertainty must be estimated at the level of the parametric value. (1) “Uncertainty of measurement” is a non-negative parameter characterising the dispersion of the quantity values being attributed to a measurement, 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 better. Measurement uncertainty must be estimated at the level of the parametric value.
(2) If the value of uncertainty of measurement cannot be met, the best available technique must be selected (up to 60% of the parametric value). (2) If the value of uncertainty of measurement cannot be met, the best available technique must be selected (up to 60% of the parametric value).
(3) The method determines total cyanide in all forms. (3) The method determines total cyanide in all forms.
(4) Reference method: European standard EN ISO 8467 entitled “Water quality - Determination of permanganate index (ISO 8467:1993)[^f00016]. (4) Reference method: European standard EN ISO 8467 entitled “Water quality - Determination of permanganate index (ISO 8467:1993)[^f00016].
(5) 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 several pesticides, higher values up to 80% may be allowed for a number of pesticides. (5) 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 several pesticides, higher values up to 80% may be allowed for a number of pesticides.
(6) The performance characteristics apply to individual substances, specified at 25% of the parametric value in Part 1 of Table B in Part 1 of Schedule 1. (6) The performance characteristics apply to individual substances, specified at 25% of the parametric value in Part 1 of Table B in Part 1 of Schedule 1.
(7) The performance characteristics apply to individual substances, specified at 50% of the parametric value in Part 1 of Table B in Part 1 of Schedule 1. (7) The performance characteristics apply to individual substances, specified at 50% of the parametric value in Part 1 of Table B in Part 1 of Schedule 1.
(8) The uncertainty of measurement must be estimated at the level of 3 mg/l of the total organic carbon (TOC) in accordance with European standard EN 1484 entitled “Water analysis - Guidelines for the determination of total organic carbon and dissolved organic carbon”[^f00017] and dissolved organic carbon (DOC) must be used. (8) The uncertainty of measurement must be estimated at the level of 3 mg/l of the total organic carbon (TOC) in accordance with European standard EN 1484 entitled “Water analysis - Guidelines for the determination of total organic carbon and dissolved organic carbon”[^f00017] and dissolved organic carbon (DOC) must be used.
(9) The uncertainty of measurement must be estimated at the level of 1.0 nephelometric turbidity units (NTU) in accordance with European standard EN ISO 7027-1 entitled “Water quality - Determination of turbidity - Part 1: Quantitative methods (ISO 7027-1:2016”[^f00018]. (9) The uncertainty of measurement must be estimated at the level of 1.0 nephelometric turbidity units (NTU) in accordance with European standard EN ISO 7027-1 entitled “Water quality - Determination of turbidity - Part 1: Quantitative methods (ISO 7027-1:2016”[^f00018].
Aluminium 25
Ammonium 40
Antimony 40
Arsenic 30
Benzene 40
Benzo(a)pyrene [^f01001] 50
Boron 25
Bromate 40
Cadmium 25
Chloride 15
Chromium 30
Colour 20
Conductivity 20
Copper 25
Cyanide [^f01002] 30
1,2-dichloroethane 40
Fluoride 20
Hydrogen ion concentration pH (expressed in pH units) 0.2
Iron 30
Lead 25
Manganese 30
Mercury 30
Nickel 25
Nitrate 15
Nitrite 20
Oxidisability [^f01003] 50
Pesticides [^f01004] 30
Polycyclic aromatic hydrocarbons [^f01005] 50
Selenium 40
Sodium 15
Sulphate 15
Tetracloroethene [^f01006] 30
Tetracloromethane 30
Trichloroethene [^f01006] 40
Trihalomethanes: total [^f01005] 40
Total organic carbon [^f01007] 30
Turbidity [^f01008] 30

referred to as “standard values and relationships” in Article 13, and recommended for the estimation of doses from internal exposure in the definition of “standard values and relationships” in Article 4(96), of Council Directive 2013/59/Euratom laying down basic safety standards for protection against the dangers arising from exposure to ionising radiation[^f00019], or

(k) a summary of any risk assessment; (l) a summary of the reasons for a decision to reduce or exempt altogether the monitoring of a particular parameter under regulation 11(10) and (10A).

Transitional and saving provisions

3

must on and after that date instead monitor in accordance with the provision made in Schedule 2 to the 2016 Regulations as amended by regulation 2(10) of these Regulations.

  • “limit of detection” is to be calculated as— three times the standard deviation within a batch of a natural sample containing a low concentration of the parameter; or five times the standard deviation of a blank sample (within a batch);
  • “precision” is to be calculated as a measure of random error and may be expressed as the standard deviation (within and between batches) of the spread of results from the mean. A precision measurement of twice the relative standard deviation is acceptable. The term “precision” is further specified in ISO 5725 entitled partly “Accuracy (trueness and precision) of measurement methods and results”[^f00020], as amended by the technical corrigendum entitled “Accuracy (trueness and precision) of measurement methods and results - Part 1: General Principles and Definitions TECHNICAL CORRIGENDUM 1”[^f00021];
  • “trueness” is to be calculated as a measure of systematic error which is the difference between the mean value of the large number of repeated measurements and the true value. The term “trueness” is further specified in ISO 5725 entitled partly “Accuracy (trueness and precision) of measurement methods and results”, as amended by the technical corrigendum entitled “Accuracy (trueness and precision) of measurement methods and results - Part 1: General Principles and Definitions TECHNICAL CORRIGENDUM 1”.

Signed

David Rutley — Parliamentary Under Secretary of State — Department for Environment, Food and Rural Affairs — 14th June 2018

Explanatory note

(This note is not part of the Regulation)

EXPLANATORY NOTE

These Regulations amend the Private Water Supplies (England) Regulations 2016 (S.I 2016/618). The amendments principally implement the requirements of Commission Directive (EU) 2015/1787 (OJ L 260, 7.10.2015, p.6) which amended Council Directive 98/83/EC on the quality of water intended for human consumption (OJ L 330, 5.12.1998, p.32). The purpose of those amendments is to align the principles applying in the EU in respect of risk based sampling and analysis of drinking water with those of the World Health Organisation.

The Regulations in particular update the requirements for monitoring programmes put in place by local authorities to monitor private water supplies of drinking water. The programmes set minimum sampling frequencies in respect of particular parameters in water intended for human consumption. The Regulations also introduce a new risk assessment approach. Where the criteria of that approach are met, local authorities are permitted to reduce the frequencies for the sampling and analysis of water. Further, the Regulations provide the specifications for the methods of analysis of certain parameters and performance characteristics of all parameters.

Regulation 3 contains transitional and saving provisions. They allow a local authority to rely on data collected before these Regulations come into force to justify any variation in the frequency of monitoring in relation to specified parameters (paragraphs (1) and (2)) and give a local authority the choice of continuing to use certain pre-existing analytical methods (with a modification) instead of the replacement methods introduced by these Regulations for any period ending before or with 31st December 2019 (paragraphs (3) to (5)).

Digital and hard copies of the British standards referred to in these Regulations published by the British Standards Institution can be purchased online from the BSI Group athttp://www.bsigroup.com. Hardcopies of the standardscan also be purchased by post from the BSI Group’s Customer Services Department at 389 Chiswick High Road, London W4 4AL (Tel: 0345 086 9001).

Digital and hard copies of the ISO standards referred to in these Regulations can be purchased online from the International Organization for Standardization (http://www.iso.org). They can also be purchased online from the BSI Group internet address mentioned above and in hard copy form from the BSI Group at the postal address mentioned above.

Copies of the British and ISO standards referred to in these Regulations are available for inspection free of charge during normal office hours at the offices of the Department for Environment, Food and Rural Affairs at the address mentioned below.

The explanatory memorandum, transposition note and impact assessment in respect of these Regulations are available in hard copy from the Water Quality Team, Department for Environment, Food and Rural Affairs, 3rd Floor, Seacole Block, 2 Marsham Street, London SW1P 4DF and published alongside these Regulations on www.legislation.gov.uk.

Footnotes

[^f00001]: 1991 c.56. Section 213(2) was amended by paragraph 28 of Schedule 1 to the Competition and Service (Utilities) Act 1992 (c.43) and by section 36(2) of, and paragraph 49(3) of Schedule 8 to, the Water Act 2003 (c.37). It has also been amended by paragraph 119(4) of Schedule 7 to the Water Act 2014 (c.21).

[^f00002]: 1972 c.68. Section 2(2) was amended by section 27(1)(a) of the Legislative and Regulatory Reform Act 2006 (c.51) and by Part 1 of the Schedule to the European Union (Amendment) Act 2008 (c.7).

[^f00003]: S.I. 2008/301.

[^f00004]: OJ No L 31, 1.2.2002, p 1, as last amended by Regulation (EU) No 652/2014 (OJ No L 189, 27.6.14 p 1).

[^f00005]: S.I. 2016/618.

[^f00006]: This standard was approved by the European Committee for Standardization (CEN) on 5th July 2013. Under reference BS EN 15975-2, it is published as a UK standard by the British Standards Institution (ISBN 978 0 580 84737 0).

[^f00007]: OJ L 327, 22.12.2000, p.1, last amended by Commission Directive 2014/101/EU (OJ L 311, 31.10.2014, p.32).

[^f00008]: This standard was approved by the International Organization for Standardization (ISO) on 15th April 2006. Under reference BS ISO 5667-5:2006 it is published as a UK standard by the British Standards Institution (ISBN 0 580 47140 3).

[^f00009]: This standard was approved by the European Committee for Standardization (CEN) on 1st July 2006. Under reference BS EN ISO 19458:2006, it is published as a UK standard by the British Standards Institution (ISBN 0 5804 49136 6).

[^f00010]: See S.I. 2009/3155 as to the establishment of the United Kingdom Accreditation Service.

[^f00011]: This standard was approved by the European Committee for Standardization (CEN) on 2nd June 2012. Under reference BS EN ISO/IEC 17024:2012, it is published as a UK standard by the British Standards Institution (ISBN 0 978 0580 78463 7).

[^f00012]: This standard was approved by the European Committee for Standardization (CEN) on 10th November 2017. Under reference BS EN ISO/IEC 17025:2005, it is published as a UK standard by the British Standards Institution (ISBN 0 580 46330 3).

[^f00013]: OJ L 201, 1.8.2009, p.36.

[^f00014]: This standard was approved by the European Committee for Standardization (CEN) on 15th July 2016. Under reference BS EN ISO 14189:2016, it is published as a UK standard by the British Standards Institution (ISBN 978 0 580 92184 1).

[^f00015]: This standard was approved by the European Committee for Standardization (CEN) on 11th January 2008. Under reference BS EN ISO 16266:2008, it is published as a UK standard by the British Standards Institution (ISBN 978 0 580 59736 7).

[^f00016]: This standard was approved by the European Committee for Standardization (CEN) on 3rd November 1994. Under reference EN ISO 8467:1995, it is published as a UK standard by the British Standards Institution (ISBN 0 580 23435 5).

[^f00017]: This standard was approved by the European Committee for Standardization (CEN) on 6th April 1997. Under reference BS EN 1484:1997, it is published as a UK standard by the British Standards Institution (ISBN 0 580 28372 0).

[^f00018]: This standard was approved by the European Committee for Standardization (CEN) on 15th April 2016. Under reference BS EN ISO 7027-1:2016, it is published as a UK standard by the British Standards Institution (ISBN 978 0 580 81961 2).

[^f00019]: OJ No L 13, 17.1.2014, p.1. For the estimation of doses from internal exposure, Article 4(96) refers to chapter 1 of ICRP (International Commission on Radiological Protection) Publication 119. See Table F.1 in Annex F. A copy of ICRP Publication 119 can be obtained from the ICRP website (www.icrp.org) or from the Water Quality Team, Department for Environment, Food and Rural Affairs, 3rd Floor, Seacole Block, 2 Marsham Street, London SW1P 4DF.

[^f00020]: This standard was published by the International Organization for Standardization (ISO) on 22nd December 1994. Under reference BS ISO 5725-1:1994 to BS ISO 5725-6:1994, it is published as UK standards by the British Standards Institution (ISBN 0 580 24034 7, 0 580 24033 9, 0 580 24029 0, 0 580 24028 2, 978 0 580 63299 0 and 0 580 24024 X).

[^f00021]: ISO 5725-1:1994/Cor 1:1998 published on 2nd May 1998.

Reading this document does not replace reading the official text published on legislation.gov.uk. Contains public sector information licensed under the Open Government Licence v3.0. We assume no responsibility for any inaccuracies arising from the conversion of the original CLML XML to this format.

This text is published under legislation.gov.uk's own terms of reuse, not a Legalize or public-domain licence. legislation.gov.uk
Open Government Licence v3.0 (attribution required)
© Crown and database right. Derived from content available under the Open Government Licence v3.0 from legislation.gov.uk.