S.I. No. 166/2022 - European Union (Water Policy) (Amendment) Regulations 2022

1. The register of protected areas required under Article 6 of the Directive and article 8 shall include the following types of protected areas

(a) areas designated for the abstraction of water intended for human consumption under Article 7 of the Directive;

(b) areas designated for the protection of economically significant aquatic species;

(c) bodies of water designated as recreational waters, including areas designated as bathing waters under Directive 2006/7/EC of the European Parliament and of the Council of 15 February 2006

2

concerning the management of bathing water quality and repealing Directive 76/160/EEC;

(d) nutrient-sensitive areas, including areas designated as –

(i) vulnerable zones under Council Directive 91/676/EEC of 12 December 1991

3

concerning the protection of waters against pollution caused by nitrates from agricultural sources, and

(ii) areas designated as sensitive areas under Council Directive 91/271/EEC of 21 May 1991

4

concerning urban waste-water treatment;

(e) areas designated for the protection of habitats or species where the maintenance or improvement of the status of water is an important factor in their protection, including relevant Natura 2000 sites designated under -

(i) Council Directive 92/43/EEC of 21 May 1992

5

on the conservation of natural habitats and of wild fauna and flora, and

(ii) Directive 2009/147/EC of the European Parliament and of the Council of 30 November 2009

6

on the conservation of wild birds.

2. The summary of the register required as part of the river basin management plan shall include maps indicating the location of each protected area and a description of the Community, national or local legislation under which they have been designated.

TENTH SCHEDULE

Articles 10A and 12

Normative Definitions of ecological status classifications

For the purposes of Parts 1 to 4 the following shall apply

(a) Waters achieving a status below moderate shall be classified as poor or bad;

(b) Waters showing evidence of major alterations to the values of the biological quality elements for the surface water body type and in which the relevant biological communities deviate substantially from those normally associated with the surface water body type under undisturbed conditions, shall be classified as poor.

(c) Waters showing evidence of severe alterations to the values of the biological quality elements for the surface water body type and in which large portions of the relevant biological communities normally associated with the surface water body type under undisturbed conditions are absent, shall be classified as bad.

Part 1

Ecological Status in Rivers

‘benthic invertebrate fauna’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.1 of Annex V to the Directive;

‘fish fauna’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.1 of Annex V to the Directive;

‘general conditions’ in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.1 of Annex V to the Directive;

‘hydrological regime’ in the context of high, good or moderate status of hydromorphological quality elements, have the respective meanings given to them in Paragraph 1.2.1 of Annex V to the Directive;

‘macrophytes and phytobenthos’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.1 of Annex V to the Directive;

‘morphological conditions’ in the context of high, good or moderate status of hydromorphological quality elements, have the respective meanings given to them in Paragraph 1.2.1 of Annex V to the Directive;

‘phytoplanton’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.1 of Annex V to the Directive;

‘specific non-synthetic pollutants’ in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.1 of Annex V to the Directive;

‘specific synthetic pollutants’ in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.1 of Annex V to the Directive;

‘river continuity’ in the context of high, good or moderate status of hydromorphological quality elements, have the respective meanings given to them in Paragraph 1.2.1 of Annex V to the Directive;

Part 2

Ecological Status in Lakes

‘benthic invertebrate fauna’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.2 of Annex V to the Directive;

‘fish fauna’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.2 of Annex V to the Directive;

‘general conditions’ in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.2 of Annex V to the Directive;

‘hydrological regime’ in the context of high, good or moderate status of hydromorphological quality elements, have the respective meanings given to them in Paragraph 1.2.2 of Annex V to the Directive;

‘morphological conditions’ in the context of high, good or moderate status of hydromorphological quality elements, have the respective meanings given to them in Paragraph 1.2.2 of Annex V to the Directive;

‘macrophytes and phytobenthos’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.2 of Annex V to the Directive;

‘phytoplanton’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.2 of Annex V to the Directive;

‘specific non-synthetic pollutants’ in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.2 of Annex V to the Directive;

‘specific synthetic pollutants’ in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.2 of Annex V to the Directive;

Part 3

Ecological Status in Transitional waters

‘angiosperms’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.3 of Annex V to the Directive;

‘benthic invertebrate fauna’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.3 of Annex V to the Directive;

‘fish fauna’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.3 of Annex V to the Directive;

‘general conditions’, in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.3 of Annex V to the Directive;

‘macroalgae’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.3 of Annex V to the Directive;

‘morphological conditions’, in the context of high, good or moderate status of hydromorphological quality elements, have the respective meanings given to them in Paragraph 1.2.3 of Annex V to the Directive;

‘phytoplanton’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.3 of Annex V to the Directive;

‘specific non-synthetic pollutants’, in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.3 of Annex V to the Directive;

‘specific synthetic pollutants’, in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.3 of Annex V to the Directive;

‘tidal regime’, in the context of high, good or moderate status of hydromorphological quality elements, have the respective meanings given to them in Paragraph 1.2.3 of Annex V to the Directive;

Part 4

Ecological Status in Coastal waters

‘benthic invertebrate fauna’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.4 of Annex V to the Directive;

‘general conditions’, in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.4 of Annex V to the Directive;

‘macroalgae and angiosperms’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.4 of Annex V to the Directive;

‘morphological conditions’, in the context of high, good or moderate status of hydromorphological quality elements, have the respective meanings given to them in Paragraph 1.2.4 of Annex V to the Directive;

‘phytoplanton’, in the context of high, good or moderate status of biological quality elements, have the respective meanings given to them in Paragraph 1.2.4 of Annex V to the Directive;

‘specific non-synthetic pollutants’, in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.4 of Annex V to the Directive;

‘specific synthetic pollutants’, in the context of high, good or moderate status of physico-chemical quality elements, have the respective meanings given to them in Paragraph 1.2.4 of Annex V to the Directive;

‘tidal regime’, in the context of high, good or moderate status of hydromorphological quality elements, have the respective meanings given to them in Paragraph 1.2.4 of Annex V to the Directive;

Part 5

Ecological Potential for Heavily Modified or Artificial Water Bodies

‘biological quality elements’, in the context of maximum, good or moderate potential for heavily modified or artificial water bodies, have the respective meanings given to them in Paragraph 1.2.5 of Annex V to the Directive.

‘hydromorphological elements’, in the context of maximum, good or moderate potential for heavily modified or artificial water bodies, have the respective meanings given to them in Paragraph 1.2.5 of Annex V to the Directive.

‘general conditions’, in the context of maximum, good or moderate potential for heavily modified or artificial water bodies, have the respective meanings given to them in Paragraph 1.2.5 of Annex V to the Directive.

‘specific non-synthetic pollutants’, in the context of maximum, good or moderate potential for heavily modified or artificial water bodies, have the respective meanings given to them in Paragraph 1.2.5 of Annex V to the Directive.

‘specific synthetic pollutants’, in the context of maximum, good or moderate potential for heavily modified or artificial water bodies, have the respective meanings given to them in Paragraph 1.2.5 of Annex V to the Directive.”.

GIVEN under my Official Seal,

31 March, 2022.

DARRAGH O’BRIEN,

Minister for Housing, Local Government and Heritage.

EXPLANATORY NOTE

(

This note is not part of the Instrument and does not purport to be a legal interpretation

)

These Regulations, made under

section 3

of the

European Communities Act 1972

(No. 27 of 1972), amend the European Communities (Water Policy) Regulations 2003 (

S.I. No. 722 of 2003

) for the purposes of giving further effect to Directive 2000/60/EC of the European Parliament and of the Council of 23 October 2000 establishing a framework for Community action in the field of water policy, as amended.

1 OJ No. L 327, 22.12.2000, p. 1

1 OJ No. L 327, 22.12.2000, p. 1

2 OJ No. L 64, 04.03.2006, p. 37

3 OJ No. L 375, 31.12.1991, p. 1

4 OJ No. L 135, 30.05.1991, p. 40

5 OJ No. L 206, 22.07.1992, p. 7

6 OJ No. L 20, 26.01.2010, p. 7

3. For those bodies of groundwater which cross the boundary of the State or are identified following the initial characterisation undertaken in accordance with paragraph (1) as being at risk of failing to meet the objectives set for each body under Article 4 of the Directive, the following information shall, where relevant, be collected and maintained for each groundwater body

(a) the location of points in the groundwater body used for the abstraction of water with the exception of the following

(i) points for the abstraction of water providing less than an average of 10 m

3

per day;

(ii) points for the abstraction of water intended for human consumption providing less than an average of 10 m

3

per day or serving less than 50 persons;

(b) the annual average rates of abstraction from such points;

(c) the chemical composition of water abstracted from the groundwater body;

(d) the location of points in the groundwater body into which water is directly discharged;

(e) the rates of discharge at such points;

(f) the chemical composition of discharges to the groundwater body;

(g) land use in the catchment from which the groundwater body receives its recharge, including pollutant inputs and anthropogenic alterations to the recharge characteristics such as rainwater and run-off diversion through land sealing, artificial recharge, damming or drainage.

Review of the impact of changes in groundwater levels

4. Following consultation with the EPA, the Minister shall identify those bodies of groundwater for which lower objectives are to be specified under Article 4 of the Directive including as a result of consideration of the effects of the status of the body on the following

(a) surface water and associated terrestrial ecosystems;

(b) water regulation, flood protection and land drainage;

(c) human development.

Review of the impact of pollution on groundwater quality

5. Following consultation with the EPA, the Minister shall identify those bodies of groundwater for which lower objectives are to be specified under Article 4(5) of the Directive where, as a result of the impact of human activity, as determined in accordance with Article 5(1) of the Directive, the body of groundwater is so polluted that achieving good groundwater chemical status is infeasible or disproportionately expensive.

EIGHTH SCHEDULE

Article 7

Economic Analysis

The economic analysis referred to in article 7(2) shall contain enough information in sufficient detail (taking account of the costs associated with collection of the relevant data) in order to –

(a) make the relevant calculations necessary for taking into account under Article 9 of the Directive the principle of recovery of the costs of water services, taking account of long term forecasts of supply and demand for water in the river basin district and, where necessary –

(i) estimates of the volume, prices and costs associated with water services, and

(ii) estimates of relevant investment including forecasts of such investments,

and

(b) make judgements about the most cost-effective combination of measures in respect of water uses to be included in the programme of measures under Article 11 of the Directive based on estimates of the potential costs of such measures.

NINTH SCHEDULE

Article 8

PROTECTED AREAS

6. Type-specific biological reference conditions based on modelling may be derived using either predictive models or hindcasting methods. The methods shall use historical, palaeological and other available data and shall provide a sufficient level of confidence about the values for the reference conditions to ensure that the conditions so derived are consistent and valid for each surface water body type.

7. Where it is not possible to establish reliable type-specific reference conditions for a quality element in a surface water body type due to high degrees of natural variability in that element, not just as a result of seasonal variations, then that element may be excluded from the assessment of ecological status for that surface water type. In such circumstances, the Minister shall state the reasons for this exclusion in the river basin management plan.

SEVENTH SCHEDULE

Article 7

GROUNDWATERS

Initial characterisation

8. The EPA shall submit to the Commission a map (in a GIS format) of the geographical location of the types consistent with the degree of differentiation required under system A.

FIFTH SCHEDULE

Fourth schedule

Ecoregions and surface water body types

1.2.1 - 1.2.4 of Annex II of Directive

9. Article 10 of the Principal Regulations is amended by inserting after subarticle (8) (inserted by Regulation 4 of the European Union Environmental Objectives (Surface Waters) (Amendment) Regulations 2015 (

S.I. No. 386 of 2015

)) the following subarticle

“ (9) Where it considers it necessary following a characterisation and impact assessment carried out under these Regulations, the EPA shall review and update monitoring programmes established under these Regulations for each period to which a river basin management plan applies.”.

Insertion of articles 10A to 10K into Principal Regulations

9A. The quality elements applicable to artificial and heavily modified surface water bodies shall be those applicable to whichever of the following natural surface water categories most closely resembles the heavily modified or artificial water body concerned

(a) rivers;

(b) lakes;

(c) transitional waters;

(d) coastal waters.

Procedure for the setting of chemical quality standards

9B. (1) In deriving environmental quality standards for pollutants listed in paragraphs 1 to 9 of Schedule 1 to the Waste Water Discharge (Authorisation) Regulations 2007 (

S.I. No. 684 of 2007

) for the protection of aquatic biota, the Minister, having consulted with the EPA, may set standards for water, sediment or biota.

(2) In setting the standards referred to in paragraph (1), where possible, both acute and chronic data shall be obtained for the taxa set out in paragraph (3) which are relevant for the water body type concerned as well as any other aquatic taxa for which data are available.

(3) The ‘base set’ of taxa, referred to in paragraph (2), are the following

(a) algae or macrophytes;

(b) daphnia or representative organisms for saline waters;

(c) fish.

Setting the environmental quality standard

9C. The following procedure applies to the setting of a maximum annual average concentration

(a) Appropriate safety factors shall be set in each case consistent with –

(i) the nature and quality of the available data and the guidance given, as may be amended by the Commission from time to time, in section 3.3.1 of Part II of the ‘Technical guidance document in support of Commission Directive 93/67/EEC on risk assessment for new notified substances and Commission Regulation (EC) No 1488/94 on risk assessment for existing substances’, and

(ii) the safety factors set out in the Table to this article;

(b) where data on persistence and bioaccumulation are available, these shall be taken into account in deriving the final value of the environmental quality standard;

(c) the standard thus derived should be compared with any evidence from field studies and where anomalies appear, the derivation shall be reviewed to allow a more precise safety factor to be calculated;

(d) the standard derived shall be subject to peer review and public consultation including to allow a more precise safety factor to be calculated.

TABLE

Safety factor

At least one acute L(E)C

50

from each of three trophic levels of the base set

1,000

One chronic NOEC (either fish or daphnia or a representative organism for saline waters)

100

Two chronic NOECs from species representing two trophic levels (fish and/or daphnia or a representative organism for saline waters and/or algae)

50

Chronic NOECs from at least three species (normally fish, daphnia or a representative organism for saline waters and algae) representing three trophic levels

10

Other cases, including field data or model ecosystems, which allow more precise safety factors to be calculated and applied

Case-by-case assessment

”.

Amendment of article 10 of Principal Regulations

10. The Principal Regulations are amended by inserting after article 10 the following articles

“

Monitoring of ecological status and chemical status for surface waters

10A. (1) The EPA shall establish and maintain a monitoring network in accordance with the requirements of subarticle (2) and article 10(1).

(2) The monitoring network, under subarticle (1), shall be designed so as to provide a coherent and comprehensive overview of ecological and chemical status within each river basin and shall permit classification of water bodies into 5 classes consistent with the normative definitions in the Tenth Schedule.

(3) River basin management plans shall provide a map showing the surface water monitoring network under this article.

(4) On the basis of the characterisation under article 7 and impact assessment carried out in accordance with articles 3 and 5, for each period to which a river basin management plan applies, the EPA shall establish a surveillance monitoring programme, an operational monitoring programme and, where appropriate, a programme of investigative monitoring.

(5) The EPA shall carry out, or make arrangements to have carried out, the following

(a) the monitoring of parameters which are indicative of the status of each relevant quality element;

(b) in selecting parameters for biological quality elements, the identification of the appropriate taxonomic level required to achieve adequate confidence and precision in the classification of the quality elements.

(6) Estimates of the level of confidence and precision of the results provided by the monitoring programmes established under this article shall be –

(a) given in the plan, and

(b) set out in accordance with the standards mentioned in article 10K.

Presentation of monitoring results and classification of ecological status and ecological potential

10B. (1) In the presentation of monitoring results and in the classification of ecological status and ecological potential, the EPA shall format the presentation in accordance with Tables 1 and 2 to this article.

(2) The EPA shall indicate, by a black dot on a relevant map, those bodies of water where failure to achieve good status or good ecological potential is due to non-compliance with one or more environmental quality standards which have been established for that body of water in respect of specific synthetic and non-synthetic pollutants (in accordance with the compliance regime concerned).

(3) In Table 2 to this article, the ecological potential classification for heavily modified and artificial water bodies is required to be represented by the lower of the values for biological and physiochemical monitoring results.

TABLE 1

Ecological status classification

Colour code

High

Blue

Good

Green

Moderate

Yellow

Poor

Orange

Bad

Red

TABLE 2

Ecological potential classification

Colour code

Artificial Water Bodies

Heavily Modified

Good and above

Equal green and light grey stripes

Equal green and dark grey stripes

Moderate

Equal yellow and light grey stripes

Equal yellow and dark grey stripes

Poor

Equal orange and light grey stripes

Equal orange and dark grey stripes

Bad

Equal red and light grey stripes

Equal red and dark grey stripes

.

Groundwater monitoring network

10C. (1) The EPA shall ensure that the groundwater monitoring network established under article 10 shall comply with the requirements of Articles 7 and 8 of the Water Framework Directive.

(2) The groundwater monitoring network, referred to in subarticle (1), shall –

(a) be designed so as to provide a reliable assessment of the quantitative status of all groundwater bodies or groups of bodies including assessment of the available groundwater resource, and

(b) provide a map showing the groundwater monitoring network in the river basin management plan concerned.

Density of monitoring sites

10D. (1) The EPA shall ensure that the groundwater monitoring network established under article 10 shall include sufficient representative monitoring points to estimate the groundwater level in each groundwater body or group of bodies taking into account short and long-term variations in recharge and, in particular, the following

(a) for groundwater bodies identified as being at risk of failing to achieve environmental objectives under article 12(1)(a), ensure sufficient density of monitoring points to assess the impact of abstractions and discharges on the groundwater level;

(b) for groundwater bodies within which groundwater flows across a boundary of the State, ensure sufficient monitoring points are provided to estimate the direction and rate of groundwater flow across the State boundary.

Monitoring frequency

10E. (1) The EPA shall conduct observations, for the purposes of the groundwater monitoring network established under article 10, at sufficient frequency to allow assessment of the quantitative status of each groundwater body or group of bodies taking into account short and long-term variations in recharge and shall comply, in particular, with the matters mentioned in subarticle (2).

(2) The matters referred to in subarticle (1) are the following

(a) for groundwater bodies identified as being at risk of failing to achieve environmental objectives under Article 4 of the Water Framework Directive, the EPA shall ensure sufficient frequency of measurement to assess the impact of abstractions and discharges on the groundwater level;

(b) for groundwater bodies within which groundwater flows across a boundary of the State, the EPA shall ensure sufficient frequency of measurement to estimate the direction and rate of groundwater flow across that boundary.

Groundwater monitoring network

10F. (1) The EPA shall ensure that the groundwater monitoring network established under article 10 is designed so as to provide a coherent and comprehensive overview of groundwater chemical status within each river basin and to detect the presence of long-term anthropogenically induced upward trends in pollutants.

(2) On the basis of the characterisation and impact assessment carried out in accordance with Article 5 of, and Annex II to, the Directive, the EPA shall establish a surveillance monitoring programme for each period to which a river basin management plan applies.

(3) The results of the programme, referred to in subarticle (2), shall be used to establish an operational monitoring programme to be applied for the remaining period of the plan.

(4) The EPA shall ensure that estimates of the level of confidence and precision of the results provided by the monitoring programmes under this article shall be given to the Minister for inclusion in the relevant river basin management plan.

Surveillance monitoring

10G. (1) Surveillance monitoring shall be carried out, by the EPA, in order to –

(a) supplement and validate the impact assessment procedure, and

(b) provide information for use in the assessment of long term trends both as a result of changes in natural conditions and through anthropogenic activity.

(2) When conducting surveillance monitoring under this article, it shall select sufficient monitoring sites for each of the following

(a) bodies identified as being at risk following the characterisation under article 7 and Section 2.2 of Annex II to the Water Framework Directive;

(b) bodies which cross a boundary of the State.

Selection of parameters

10H. (1) The following set of core parameters shall be monitored in all the selected groundwater bodies under article 10G(2)

(a) oxygen content;

(b) pH value;

(c) conductivity;

(d) nitrate;

(e) ammonium.

(2) Bodies which are identified in accordance with Annex II to the Directive as being at significant risk of failing to achieve good status shall also be monitored for those parameters which are indicative of the impact of those pressures.

(3) Transboundary water bodies shall also be monitored for those parameters which are relevant for the protection of all of the uses supported by the groundwater flow.

Operational monitoring

10I. (1) The EPA shall undertake operational monitoring in the periods between surveillance monitoring programmes in order to -

(a) establish the chemical status of all groundwater bodies or groups of bodies determined as being at risk, and

(b) establish the presence of any long term anthropogenically induced upward trend in the concentration of any pollutant.

(2) Operational monitoring shall be carried out by the EPA for all those groundwater bodies or groups of bodies which on the basis of both the impact assessment carried out in accordance with Annex II to the Directive and surveillance monitoring under article 10 are identified as being at risk of failing to meet objectives under Article 4 of the Directive.

(3) The selection of monitoring sites by the EPA, under this article, shall also reflect an assessment of how representative monitoring data from that site is of the quality of the relevant groundwater body.

(4) Operational monitoring shall be carried out by the EPA for the periods between surveillance monitoring programmes at a frequency sufficient to detect the impacts of relevant pressures but at a minimum of once per annum.

Identification of trends in pollutants

10J. (1) The EPA shall use data from both surveillance monitoring, under article 10G, and operational monitoring, under article 10I, in the identification of long term anthropogenically induced upward trends in pollutant concentrations and the reversal of such trends.

(2) The base year or period from which trend identification under subarticle (1) is to be calculated shall be identified.

(3) The calculation of trends shall be undertaken by the EPA for a body or, where appropriate, group of bodies of groundwater.

(4) Reversal of a trend shall be demonstrated statistically by the EPA and it shall state the level of confidence associated with the identification.

Standards for monitoring of quality elements

10K. The EPA shall ensure that the methods used for type parameters shall –

(a) conform to the international standards listed in the Tables to this article in so far as they cover monitoring, or

(b) to such other national or international standards in a manner that shall ensure the provision of data of an equivalent scientific quality and comparability.

TABLE 1 - Standards for sampling of biological quality elements

Generic methods for use with the specific methods given in the standards relating to the following biological quality elements

EN ISO 5667-3:2012

Water quality — Sampling — Part 3: Preservation and handling of samples

TABLE 2 - Standards for phytoplankton

EN 15204:2006

Water quality — Guidance standard on the enumeration of phytoplankton using inverted microscopy (Utermöhl technique)

EN 15972:2011

Water quality — Guidance on quantitative and qualitative investigations of marine phytoplankton

ISO 10260:1992

Water quality — Measurement of biochemical parameters —Spectrometric determination of the chlorophyll-a concentration

TABLE 3 - Standards for macrophyte and phytobenthos

EN 15460:2007

Water quality — Guidance standard for the surveying of macrophytes in lakes

EN 14184:2014

Water quality — Guidance for the surveying of aquatic macrophytes in running waters

EN 15708:2009

Water quality — Guidance standard for the surveying, sampling and laboratory analysis of phytobenthos in shallow running water

EN 13946:2014

Water quality — Guidance for the routine sampling and preparation of benthic diatoms from rivers and lakes

EN 14407:2014

Water quality — Guidance for the identification and enumeration of benthic diatom samples from rivers and lakes

TABLE 4 - Standards for benthic invertebrate

EN ISO 10870:2012

Water quality — Guidelines for the selection of sampling methods and devices for benthic macroinvertebrates in fresh waters

EN 15196:2006

Water quality — Guidance on sampling and processing of the pupal exuviae of Chironomidae (order Diptera) for ecological assessment

EN 16150:2012

Water quality — Guidance on pro rata multi-habitat sampling of benthic macro-invertebrates from wadeable rivers

EN ISO 19493:2007

Water quality — Guidance on marine biological surveys of hard-substrate communities

EN ISO 16665:2013

Water quality — Guidelines for quantitative sampling and sample processing of marine soft-bottom macro-fauna

TABLE 5 - Standards for fish

EN 14962:2006

Water quality — Guidance on the scope and selection of fish sampling methods

EN 14011:2003

Water quality — Sampling of fish with electricity

EN 15910:2014

Water quality — Guidance on the estimation of fish abundance with mobile hydroacoustic methods

EN 14757:2005

Water quality — Sampling of fish with multi-mesh gillnets

TABLE 6 - Standards for hydromorphological parameters

EN 14614:2004

Water quality — Guidance standard for assessing the hydromorphological features of rivers

EN 16039:2011

Water quality — Guidance standard on assessing the hydromorphological features of lakes

EN 1650:2014

Water quality – Guidance standard for assessing the hydromorphological features of transitional and costal waters

TABLE 7 - Standards for physico-chemical parameters

Any relevant CEN/ISO standards”.

Amendment of article 12(1) of Principal Regulations

11. Article 12(1) (amended by Regulation 5 of the European Union Environmental Objectives (Surface Waters) (Amendment) Regulations 2015 (

S.I. No. 386 of 2015

)) of the Principal Regulations is amended by the substitution of the following subparagraphs for subparagraph (a)

“(a) establish environmental objectives in relation to each river basin district in accordance with Article 4 of the Directive and, in the case of any particular objective relating to a given body of water, the most stringent requirement in that Article shall apply,

(ab) Where monitoring or other data indicate that the objectives set under Article 4 of the Directive for the body of water concerned are unlikely to be achieved –

(i) the relevant local authority shall ensure that the causes of the possible failure are investigated,

(ii) the relevant local authority shall ensure that the relevant permits and authorisations are examined and reviewed as appropriate,

(iii) the EPA shall ensure that the monitoring programmes are reviewed and adjusted as appropriate, and

(iv) the Minister shall ensure that the additional measures as may be necessary in order to achieve those objectives are established, including, as appropriate, the establishment of stricter environmental quality standards following the procedures laid down in Annex V to the Directive,

(ac) Where –

(i) the objectives set under Article 4 of the Directive for the body of water concerned are unlikely to be achieved and such failures are the result of circumstances of natural cause or force majeure which are exceptional and could not reasonably have been foreseen, in particular extreme floods and prolonged droughts, subject to Article 4(6) of the Directive, and

(ii) the EPA has advised the Minister that additional measures are not practicable,

the Minister shall –

(I) adopt such further supplementary measures as he or she considers necessary to ensure that all practicable steps are taken to prevent further deterioration in status and in order not to compromise the objectives of the Directive in other bodies of water not affected by those circumstances, and

(II) include those further supplementary measures in next update of the river basin management plan concerned.

(ad) In implementing measures pursuant to this article, the local authority concerned shall take all appropriate steps not to increase pollution of marine waters,

(ae) Without prejudice to existing legislation, the application of measures taken pursuant to this article may on no account lead, either directly or indirectly, to increased pollution of surface water and this requirement shall not apply where it would result in increased pollution of the environment as a whole,

(af) The Minister shall ensure that the programmes of measures under these Regulations shall be established at the latest 9 years after the date of entry into force of the Directive and all the measures shall be made operational at the latest 12 years after that date,”.

Amendment of article 12(2) of Principal Regulations

12. Article 12 of the Principal Regulations is amended by the substitution of the following subarticle for subarticle (2)

“(2) A programme of measures shall include –

(a) the basic measures specified in Article 11(3) of the Directive,

(b) such supplementary measures specified in Article 11(4) of the Directive as the relevant authorities consider appropriate, and

(c) the legislation specified in Article 10 of, and Annex VI to, the Directive.”.

Amendment of article 12 of Principal Regulations

13. Article 12 of the Principal Regulations (as amended by Regulation 7 of the European Union (Water Policy) Regulations 2014 (

S.I. No. 350 of 2014

)) is amended by inserting after subarticle (2) the following subarticles

“(3) The Minister shall establish the programmes of measures under these Regulations not later than 9 years after the date of entry into force of the Directive and all the measures shall be made operational not later than 12 years after that date of entry into force.

(4) The Minister shall review the programmes of measures and, if necessary, update them at the latest 15 years after the date of entry into force of the Directive and every 6 years thereafter and any new or revised measures established under an updated programme shall be made operational not later than 3 years after the date of their establishment.”.

Amendment of article 13 of Principal Regulations

14. Article 13 of the Principal Regulations (as amended by Regulation 8 of the European Union (Water Policy) Regulations 2014 (

S.I. No. 350 of 2014

)) is amended by inserting after subarticle (4) the following subarticle

“(5) The Minister shall review and update the river basin management plans not later than 15 years after the date of entry into force of the Directive and every 6 years thereafter.”.

Amendment of article 14 of Principal Regulations

15. Article 14 of the Principal Regulations (as amended by Regulation 9 of the European Union (Water Policy) Regulations 2014 (

S.I. No. 350 of 2014

)) is amended by the substitution of the following subarticles for subarticles (1) and (2)

“ (1) The Minister shall, subject to paragraph (3), in accordance with Article 14 of the Directive and supported by the EPA and with the assistance of local authorities working at both local and regional level, prepare and publish for each river basin district the following

(a) not later than 3 years before the beginning of the period to which the plan relates, a timetable and work programme for the production of a river basin management plan, including a statement as to the consultation measures to be taken;

(b) not later than 2 years before the beginning of the period to which the plan relates, an interim overview of the significant water management issues identified in river basin districts;

(c) not later than one year before the beginning of the period to which the plan relates, draft copies of the river basin management plans.

(2) On publication of the documents specified in subarticle (1), in order to allow active involvement and consultation, the Minister shall by notice published in a daily newspaper circulating in the river basin district concerned, invite the provision of comments in writing by any person and shall allow a period of not less than 6 months for the provision of such comments.

(3) The Minister shall ensure that appropriate administrative arrangements under this Regulation are in place for the application of the Directive to any portion of any international river basin in the State.”.

Insertion of Fourth to Tenth Schedules to Principal Regulations

16. The Principal Regulations are amended by inserting after the Third Schedule the following Schedules

“

FOURTH SCHEDULE

Article 7

Characterisation of surface water body types

SURFACE WATERS

Notice of the making of this Statutory Instrument was published in

“Iris Oifigiúil” of

5

th April,

2022.

CONTENTS

Regulation

PART 1

PRELIMINARY AND GENERAL