The Surface Waters (Fishlife) (Classification) Regulations (Northern Ireland) 1997

Type Ni-Statutory-Rule
Publication 1997-11-12
State In force
Jurisdiction Northern Ireland
Department Government Printer for Northern Ireland
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Made: 12th November 1997

Coming into operation: 5th January 1998

The Department of the Environment, in exercise of the powers conferred on it by section 4B of the Water Act (Northern Ireland) 1972[^f00001] and now vested in it[^f00002], section 56B of the Water and Sewerage Services (Northern Ireland) Order 1973[^f00003] and, being a department designated[^f00004] for the purposes of section 2(2) of the European Communities Act 1972[^f00005] in relation to measures relating to the prevention, reduction and elimination of pollution of water, in exercise of the powers conferred on it by that section and of every other power enabling it in that behalf, hereby makes the following Regulations:

Citation and commencement

1

This Order may be cited as the The Surface Waters (Fishlife) (Classification) Regulations (Northern Ireland) 1997 and shall come into operation on 5th January 1998.

Interpretation

2

Classification of waters

3

The classifications SW (“salmonid waters”) and CW (“cyprinid waters”), and the criteria for those classifications, set out in Schedule 1 shall apply for classifying fresh waters which need protection or improvement in order to support fish life.

Compliance with relevant requirements

4

Guideline values and no deterioration principle

5

In discharging its pollution control functions in relation to any waters classified under these Regulations, the Department shall—

Compliance with standards

6

Sampling and Analysis

7

Derogations

8

Modification of section 4C of the Water Act (Northern Ireland) 1972

9

Section 4C of the Water Act (Northern Ireland) 1972 shall have effect—

Programmes

10

The Department shall establish programmes in order to reduce pollution and to ensure that waters classified under these Regulations conform, within 5 years following classification, to the criteria set out in Schedule 1 and to the values adopted as a result of regulation 5.

Transfrontier Consultation

11

SCHEDULE 1

Part I — Criteria for classification of water as salmonid and cyprinid waters

1

Temperature measured downstream of a point of thermal discharge (at the edge of the mixing zone) must not exceed the unaffected temperature by more than 1.5°C for salmonid waters and 3°C for cyprinid waters.Derogations limited in geographical scope may be decided by the Department in particular conditions if it can prove that there are no harmful consequences for the balanced development of the fish population.

2

Thermal discharges must not cause the temperature downstream of the point of thermal discharge (at the edge of the mixing zone) to exceed—

Temperature limits may, however, be exceeded for 2% of the time.

Part II — Zinc concentrations (mg/1 Zn) for different water hardness value between 10 and 500 mg/l CaCO3

Water hardness (mg/1 CaCO) Water hardness (mg/1 CaCO) Water hardness (mg/1 CaCO) Water hardness (mg/1 CaCO)
10 50 100 500
Salmonid waters (mg/1 Zn) 0.03 0.2 0.3 0.5
Cyprinid waters (mg/1 Zn) 0.3 0.7 1.0 2.0

SCHEDULE 2

Part I — Guideline values in relation to the quality of salmonid and cyprinid waters

No in Annex 1 to 78/659/EEC Parameter Salmonid waters (guideline values and comments) Cyprinid waters (guideline values and comments) Methods of analysis or inspection Minimum sampling and measuring frequency Observations
2. Dissolved oxygen (mg/1O₂) 50%≥9 100%≥7 50%≥8 100%≥5 Winkler’s method or specific electrodes (electro- chemical method) Monthly, minimum sample represent- ative of low oxygen conditions on the day of sampling. However, where major daily variations are suspected, a minimum of 2 samples in 1 day shall be taken
4. Suspended solids (mg/1) ≤25(O) ≤25(O) Filtration through a 0.45μm filtering membrane, or centrifugation (5 minutes minimum, average acceleration of 2,800 to 3,200g) drying at 105°C and weighing The values shown are average concentrations and do not apply to suspended solids with harmful chemical properties Floods are liable to cause particularly high concentrations
5. BOD₅ (mg/1O₂) ≤3 ≤6 Determination of O₂ by the Winkler method before and after 5 days incubation in complete darkness at 20°C ±1°C (nitrification should not be inhibited)
7. Nitrites (mg/1 NO₂) ≤0.01 ≤0.03 Molecular absorption spectro- photometry
10. Non-ionized ammonia (mg/1 NH₃) ≤0.005 ≤0.005 Molecular absorption spectro- photometry using indophenol blue or Nessler’s method associated with pH and temperature determ-ination Monthly Values for non-ionized ammonia may be exceed in the form of minor peaks in the daytime.
11. Total ammonium (mg/1 NH₄) In order to diminish the risk of toxicity due to non-ionised ammonia, of oxygen consumption due to nitrification and of eutrophication, the concentrations of total ammonium should not exceed 0.04 mg/1 for salmonid waters and 0.2 mg/1 for cyprinid waters In order to diminish the risk of toxicity due to non-ionised ammonia, of oxygen consumption due to nitrification and of eutrophication, the concentrations of total ammonium should not exceed 0.04 mg/1 for salmonid waters and 0.2 mg/1 for cyprinid waters
14. Dissolved copper (mg/1 Cu) ≤0.04 ≤0.04 Atomic absorption spectrometry The values correspond to a water hardness of 100 mg/1 CaCO₃ For hardness levels between 10 and 300 mg/1 corresponding limit values can be found in Part II of this Schedule

Part II — Copper concentrations (mg/1 Cu) for different water hardness values between 10 and 500 mg/l CaCO3

Water hardness (mg/1 CaCO) Water hardness (mg/1 CaCO) Water hardness (mg/1 CaCO) Water hardness (mg/1 CaCO)
(1) The presence of fish in waters containing higher concentrations of copper may indicate a predominance of dissolved organo-cupric complexes. (1) The presence of fish in waters containing higher concentrations of copper may indicate a predominance of dissolved organo-cupric complexes. (1) The presence of fish in waters containing higher concentrations of copper may indicate a predominance of dissolved organo-cupric complexes. (1) The presence of fish in waters containing higher concentrations of copper may indicate a predominance of dissolved organo-cupric complexes. (1) The presence of fish in waters containing higher concentrations of copper may indicate a predominance of dissolved organo-cupric complexes.
10 50 100 500
mg/1 Cu 0.005[^f01000] 0.02 0.04 0.112

Signed

Sealed with the Official Seal of the Department of the Environment on

R. W. Rogers — Assistant Secretary — 12th November 1997.

Explanatory note

(This note is not part of the Regulations.)

These Regulations prescribe a system for classifying the quality of freshwaters which need protection or improvement in order to support fish life.

The classifications SW (“salmonid waters”) and CW (“cyprinid waters”) prescribed by regulation 3 reflect the mandatory values assigned by Directive 78/659/EEC (“the Directive”) (on the quality of fresh waters needing protection or improvement in order to support fish life) to the parameters listed in Schedule 1 to these Regulations. Regulation 4 sets out the circumstances in which classified waters shall be treated as complying with the requirements specified in Schedule 1.

Regulation 5 requires the Department, in discharging its pollution control functions, to endeavour to observe the values and comments set out in Schedule 2 while preventing any increase in pollution. Regulation 6 sets out the circumstances in which classified waters shall be treated as complying with any standard adopted by the Department under regulation 5.

Regulation 7 makes provision with respect to the reference methods of measurement, and the minimum frequency required for sampling and analysis, laid down in the Directive for those parameters.

Regulation 8 allows the Department to derogate from the requirements of the Regulations in the event of exceptional weather or geographic conditions.

Regulation 9 modifies the Water Act (Northern Ireland) 1972 so as to require the Department to classify appropriate waters in accordance with the Directive and to remove rights of appeal against such classifications.

Regulation 10 provides for pollution reduction programmes and regulation 11 provides for consultation with the Republic of Ireland if the Department considers classifying waters in the vicinity of the frontier.

These Regulations transpose in part the requirements of Directive 78/659/EEC. Copies of the Directive may be obtained from The Stationery Office Ltd, 16 Arthur Street, Belfast BT1 4GD.

Footnotes

[^f00001]: 1972 c. 5 (N.I.) as amended by the Water and Sewerage Services (Amendment) (Northern Ireland) Order 1993 (S.I. 1993/3165 (N.I. 16) Art. 16)

[^f00002]: S.R. & O. (N.I.) 1973 No. 504 Art. 4

[^f00003]: S.I. 1973/70 (N.I.2) as amended by the Water and Sewerage Services (Amendment) (Northern Ireland) Order 1993 (S.I. 1993/3165 (N.I. 16) Art. 12)

[^f00004]: S.I. 1989/2393

[^f00005]: 1972 c. 68

[^f00006]: O.J. No. L. 222, 14. 8. 1978, p. 1

[^f00007]: 1954 c. 33 (N.I.)

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