S.I. No. 258/1998 - Local Government (Water Pollution) Act, 1977 (Water Quality Standards For Phosphorus) Regulations, 1998

Type Statutory Instrument
Publication 1998-07-24
Last updated 2009-07-24
State Repealed superseded text
Text As published
articles 4

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.

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S.I. No. 258 of 1998.

LOCAL GOVERNMENT (WATER POLLUTION) ACT, 1977 (WATER QUALITY STANDARDS FOR PHOSPHORUS) REGULATIONS, 1998

In exercise of the powers conferred on the Minister for the Environment and Local Government by section 30 of the Local Government (Water Pollution) Act, 1977 (No. 1 of 1977) and by section 26 of that Act as amended by sections 18 and 29 of the Local Government (Water Pollution) (Amendment) Act, 1990 (No. 21 of 1990), which said powers are delegated to me by the Environment and Local Government (Delegation of Ministerial Functions) (No. 2) Order, 1997 ( S.I. No. 428 of 1997 ), and for the purpose of giving further effect to provisions of Council Directive 76/464/EEC of 4 May, 1976 on pollution caused by certain dangerous substances discharged into the aquatic environment, I, Dan Wallace, Minister of State at the Department of the Environment and Local Government, hereby make the following Regulations:

1.

1.

These Regulations may be cited as the Local Government (Water Pollution) Act, 1977 (Water Quality Standards for Phosphorus) Regulations, 1998.

2.

2.

In these Regulations—

any reference to a Schedule or article which is not otherwise identified is a reference to a Schedule or article of these Regulations;

any reference to a sub-article or paragraph which is not otherwise identified is a reference to a sub-article or paragraph of the provision in which the reference occurs;

"the Principal Act" means the Local Government (Water Pollution) Act, 1977 as amended by the Local Government (Water Pollution) (Amendment) Act, 1990 ;

"the Act of 1992" means the Environmental Protection Agency Act, 1992 (No. 7 of 1992);

"the Agency" means the Environmental Protection Agency established under section 19 of the Act of 1992;

"best available technology not entailing excessive costs" has the meaning assigned to it by section 5 of the Act of 1992;

"biological quality rating" means a rating of water quality for any part of a river based principally on the composition of macroinvertebrate communities/faunal groups present and their general sensitivity to organic pollution, as used by the Agency and described in the First Schedule;

"existing biological quality rating" means, in relation to any particular part of a river, the biological quality rating for that part of the river assigned by the Agency based on monitoring carried out during the period commencing on the 1st day of 1995 and ending on the last day of 1997, or, where monitoring was not carried out during that period, the biological quality rating first assigned by the Agency to that part based on monitoring carried out after 1997;

"existing trophic status" means, in relation to any particular part of a lake, the trophic status for that part of the lake assigned by the Agency based on monitoring carried out during the period commencing on the 1st day of 1995 and ending on the last day of 1997, or, where monitoring was not carried out during that period, the trophic status first assigned by the Agency to that part based on monitoring carried out after 1997;

"the Minister" means the Minister for the Environment and Local Government;

"trophic status" means the status of lake water quality determined by the Agency in accordance with the classification system used by it and described in the Second Schedule.

3.

3.

(1) Subject to sub-article (2) concerning the improvement of water quality, the existing biological quality rating for any part of a river shall be maintained.

4.

4.

(1) A local authority shall take all such steps as may be appropriate in discharge of its functions under the Principal Act and the Agency shall take all such steps as may be appropriate in discharge of its functions under the Act of 1992 to secure compliance with the quality standards prescribed in article 3.

FIRST SCHEDULE

Biological Quality Rating System for Rivers

Part I

Indicator Groups: Key Taxa

Macroinvertebrate Communities/Faunal Groups and their General Sensitivity to Organic Pollution Macroinvertebrate Communities/Faunal Groups and their General Sensitivity to Organic Pollution Macroinvertebrate Communities/Faunal Groups and their General Sensitivity to Organic Pollution Macroinvertebrate Communities/Faunal Groups and their General Sensitivity to Organic Pollution Macroinvertebrate Communities/Faunal Groups and their General Sensitivity to Organic Pollution Macroinvertebrate Communities/Faunal Groups and their General Sensitivity to Organic Pollution
Group A Group B Group C Group D Group E Group E
Sensitive Less Sensitive Tolerant Very Tolerant Most Tolerant Most Tolerant
Perlidae Leuctridae Tricladida Hirudinea Tubificidae Tubificidae
Nemouridae Ancylidae Mollusca (excl. Ancylidae, Margaritiferidae, Neritidae & Unionidae) Chironomus Chironomus
Chloroperlidae Taeniopterygidae Neritidae Mollusca (excl. Ancylidae, Margaritiferidae, Neritidae & Unionidae) Chironomus Chironomus
Baetidae Unionidae Mollusca (excl. Ancylidae, Margaritiferidae, Neritidae & Unionidae) Chironomus Chironomus
Capniidae Leptophlebiidae Astacidae Mollusca (excl. Ancylidae, Margaritiferidae, Neritidae & Unionidae) Chironomus Chironomus
Ephemerellidae
Perlodidae Ephemeridae Gammarus Asellus
Potamanthidae Caenidae Chironomidae(excl. Chironomus & Rheotanytarsus)
Heptageniidae Cased Trichoptera (excl. Limnephilidae Hydroptilidae & Glossosomatidae) Limnephilidae Chironomidae(excl. Chironomus & Rheotanytarsus)
Cased Trichoptera (excl. Limnephilidae Hydroptilidae & Glossosomatidae) Hydroptilidae
Siphlonuridae Cased Trichoptera (excl. Limnephilidae Hydroptilidae & Glossosomatidae) Glossosomatidae
Margaritiferidae Uncased Trichoptera
Odonata(excl. Coenagriidae) Coleoptera
Coenagriidae
Sialidae
Tipulidae
Aphelocheirus Simuliidae
Rheotanytarsus Hemiptera (excl. Aphelocheirus)
Hydracarina

Part II Relationship between Biological Quality Rating/Index (Q) and the Five Faunal Groups **

Q Index Faunal Group Faunal Group Faunal Group Faunal Group Faunal Group
A B C D E
Eroding Substrata (i.e. the shallower, faster-flowing areas) Q5 # # ++ +/- +/-
Eroding Substrata (i.e. the shallower, faster-flowing areas) Q4 ++ # ++ +/-
Eroding Substrata (i.e. the shallower, faster-flowing areas) Q3 - +/-* # ++
Q2 - - +/- #
Q1 - - - +/- #
(*excl. B. rhodani which may be dominant) (*excl. B. rhodani which may be dominant) (*excl. B. rhodani which may be dominant) (*excl. B. rhodani which may be dominant) (*excl. B. rhodani which may be dominant)
Depositing Substrata (i.e. the deeper, slower-flowing areas) Q5 ++ # ++ ++
Depositing Substrata (i.e. the deeper, slower-flowing areas) Q4 +/- # ++ ++
Depositing Substrata (i.e. the deeper, slower-flowing areas) Q3 - - ++
Q2 - - -
Q1 - - - - #
--- --- ---
# = Numerous or dominant ++ = Present in small numbers
+ = Scarce +/- = Scarce or absent. - = Absent

** See "Observations on Q determination scheme" below.

Observations on Q determination scheme

1) The above scheme outlines the typical macroinvertebrate composition of rivers and streams unaffected (Q5) or variously affected (Q4 to Q1) by organic waste inputs.

2) All available habitats should be sampled and, in addition to kick sampling, stone washing and weed sweeps should be carried out where possible.

3) Single specimens may be ignored as they are likely to have drifted from upstream.

4) Q5 only ascribed in absolutely pristine conditions with diverse and balanced faunal community.

5) Providing that sewage fungus and other slime growths are absent and that Cladophora is either absent (Q5) or, if present, not excessive in development (Q4), Q5 and Q4 may be ascribed where faunal criteria are not met because of:—

a)

ground-water input

b)

very hard, calcareous conditions

c)

very oligotrophic conditions

6) The terms "Taxon/Taxa" are defined by the level of identification for each macroinvertebrate Class/Order as follows :—

platyhelminthes genus
Oligochaeta family
Hirudinea genus
Mollusca genus
Crustacea genus
Plecoptera genus
Ephemeroptera genus
Trichoptera genus
Odonata genus
Megaloptera genus
Hemiptera genus
Coleoptera family
Diptera family
(Chironomidae Chironomus, Rheotanytarsus, Other Chironomidae) (Chironomidae Chironomus, Rheotanytarsus, Other Chironomidae)
Hydracarina presence
--- ---
Abundance Category Approximate Frequency of Occurrence
Number* Percentage
One 1
Scarce/Few 2 - 5
Present in small numbers 6 - 10
Present in fair numbers 11 - 20
Common 21 - 50
Numerous 51 - 100
Abundant / Dominant 100 - 200
Superabundant / Excessive 200+

*Per 2 minute sample.

Part III Indicative Characteristics of the various Biological Quality Classes

Quality Classes Class A Class A Class B Class C Class D Class D
Quality ratings (Q) Q5 Q4 Q3-4 Q3 Q2 Q1
Pollution Status Pristine, Unpolluted. Unpolluted. Slight pollution. Moderate pollution. Heavy pollution. Gross pollution.
Organic Waste Load None. None. Light. Considerable. Heavy. Excessive.
Maximum B.O.D. Low ( Low ( Occasionally elevated High at times. Usually high. Usually very high.
Dissolved Oxygen Close to 100% at all times 80% - 120% Fluctuates from 120% Very unstable. Potential fish-kills. Low, sometimes zero. Very low, often zero.
Annual Median PO4 0.015 mg/l 0.03 mg/l 0.045 mg/l 0.07 mg/l >0.1 mg/l >0.1 mg/l
Siltation None. May be light. May be light. May be considerable. Usually heavy. Usually very heavy and anaerobic.
'Sewage Fungus' Never. Never Never May be some. Usually abundant. May be abundant.
Filamentous Algae Limited development. Considerable growths. Diverse communities. Luxuriant growths typically Cladophora. Excessive growths typically Cladophora. Usually abundant. None.
Macrophytes Diverse communities. Limited growths. Diverse communities. Considerable growths. Reduced diversity. Luxuriant growths. Limited diversity. Excessive growth. Tolerant species only. May be abundant. Usually none or tolerant species only.
Macroinvertebrates (from shallow riffles) Diverse communities. Normal density. Sensitive forms usually numerous. High diversity Increased density Sensitive forms scarce or common Very high diversity. Very high diversity. Sensitive forms scarce. Sensitive forms absent. Tolerant forms common. Low diversity Tolerant forms only. Very low diverisity. Most tolerant forms. Minimal diversity.
Water Quality Highest quality. Fair quality. Variable quality. Doubtful quality. Poor quality. Bad quality.
Abstraction Potential Suitable for all. Suitable for all. Potential problems. Advanced treatment. Low grade abstractions. Extremely limited.
Fishery Potential Game fisheries. Good game fisheries. Game fish at risk. Coarse fisheries. Fish usually absent. Fish absent.
Amenity Value Very high. High. Considerable. Reduced. Low. Zero.
Condition Satisfactory. Satisfactory. Transitional. Unsatisfactory. Unsatisfactory. Unsatisfactory.

SECOND SCHEDULE

Trophic Classification System for Lakes

Lake Trophic Category Annual Maximum Chlorophyll mg/m3 Probability of pollution
Ultra-Oligotrophic None
Oligotrophic ≥2.5 < 8 None
Mesotrophic ≥ 8 < 25 Low
Eutrophic* ≥25 Moderate-Substantial
Hypertrophic ≥75 High

*Sub-categories may be assigned in respect of moderately, strongly and highly eutrophic lakes.

THIRD SCHEDULE

PART I QUALITY STANDARDS FOR RIVERS

Column 1 Column 2 Column 3
Existing Biological Quality (Q) Rating/Q Index Minimum Target Biological Quality (Q) Rating/Q Index Molybdate-Reactive Phosphate Median Concentration*(ugP/L)
Unpolluted
5 5 15
4-5 4-5 20
4 4 30
Slightly Polluted
3-4 4 30
Moderately Polluted
3 3 - 4 50
2-3 3 70
Seriously Polluted
≤2 3 70

*Median concentration to be determined using as a minimum ten samples taken at intervals of four weeks or longer in any twelve consecutive month period. Where the requisite number of samples has not been taken within such period, the median concentration shall be determined from sampling conducted over such period, being a period not exceeding twenty four months, as required to obtain a minimum of fifteen samples taken at intervals of four weeks or longer.

PART II QUALITY STANDARDS FOR LAKES

Column 1 Column 2 Column 3
Existing Trophic Status Minimum Target Trophic Status Total Phosphorus Average Concentration* (ug P/L)
Satisfactory
Ultra-Oligotrophic Ultra-Oligotrophic ≤5
Oligotrophic Oligotrophic >5 ≤ 10
Mesotrophic Mesotrophic < 10≤ 20
Unsatisfactory
Eutrophic Mesotrophic < 10≤20
Hypertrophic Eutrophic < 20≤50

*Average concentration to be determined using as a minimum ten samples taken at intervals of four weeks or longer in any twelve consecutive month period. Where the requisite number of samples has not been taken within such period, the average concentration shall be determined from sampling conducted over such period being a period not exceeding twenty four months, as required to obtain a minimum or fifteen samples taken at intervals of four weeks or longer.

DATED this 24th day of July, 1998

Dan Wallace

Minister of State at the Department of the Environmental and Local Government.

EXPLANATORY NOTE

These Regulations provide for specified improvements in water quality conditions in rivers and lakes based on phosphorus concentrations or related water quality classifications. The Regulations also provide for periodic reporting in relation to progress in implementing the requirements of the Regulations.

These Regulations give effect to certain requirements arising under Council Directive 76/46/EC on pollution caused by certain dangerous substances discharged into the aquatic environment of the Community.

This document does not substitute the official text published in the Irish Statute Book. We accept no responsibility for any inaccuracies arising from the transcription of the original into this format.

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