Directive 2006/44/EC of the European Parliament and of the Council (repealed)Show full title

ANNEX I U.K. LIST OF PARAMETERS

a Artificial pH variations with respect to the unaffected values shall not exceed ±0,5 of a pH unit within the limits falling between 6,0 and 9,0 provided that these variations do not increase the harmfulness of other substances present in the water.
b Phenolic compounds must not be present in such concentrations that they adversely affect fish flavour.
c Petroleum products must not be present in water in such quantities that they: form a visible film on the surface of the water or form coatings on the beds of water-courses and lakes, impart a detectable ‘hydrocarbon’ taste to fish, produce harmful effects in fish.
d In particular geographical or climatic conditions and particularly in cases of low water temperature and of reduced nitrification or where the competent authority can prove that there are no harmful consequences for the balanced development of the fish population, Member States may fix values higher than 1 mg/l.
Parameter	Salmonid waters		Cyprinid waters		Methods of analysis or inspection	Minimum sampling and measuring frequency	Observations
	G	I	G	I
1. Temperature (°C)	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:			Thermometry	Weekly, both upstream and downstream of the point of thermal discharge	Over-sudden variations in temperature shall be avoided
		1,5 °C		3 °C
		Derogations limited in geographical scope may be decided by Member States in particular conditions if the competent authority 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 the following:
		21,5 (0)		28 (0)
		10 (0)		10 (0)
		The 10 °C temperature limit applies only to breeding periods of species which need cold water for reproduction and only to waters which may contain such species
		Temperature limits may, however, be exceeded for 2 % of the time.
2. Dissolved oxygen (mg/l O2)	50 % ≥ 9 100 % ≥ 7	50 % ≥ 9	50 % ≥ 8 100 % ≥ 5	50 % ≥ 7	Winkler's method or specific electrodes (electro-chemical method)	Monthly, minimum one sample representative of low oxygen conditions of the day of sampling However, where major daily variations are suspected, a minimum of two day samples in one day shall be taken
		When the oxygen concentration falls below 6 mg/l, Member States shall implement the provisions of Article 7(3). The competent authority must prove that this situation will have no harmful consequences for the balanced development of the fish population		When the oxygen concentration falls below 4 mg/l, Member States shall implement the provisions of Article 7(3). The competent authority must prove that this situation will have no harmful consequences for the balanced development of the fish population
3. pH		6 to 9 (0)a		6 to 9 (0)a	Electrometry calibration by means of two solutions with known pH values, preferably on either side of, and close to the pH being measured	Monthly
4. Suspended solids (mg/l)	≤ 25 (0)		≤ 25 (0)		Filtration through a 0,45 μm filtering membrane, or centrifugation (five minutes minimum, average acceleration of 2 800 to 3 200 g) 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/l O2)	≤ 3		≤ 6		Determination of O2 by the Winkler method before and after five days incubation in complete darkness at 20 ± 1 °C (nitrification should not be inhibited)
6. Total phosphorus (mg/l P)					Molecular absorption spectrophotometry		In the case of lakes of average depth between 18 and 300 m, the following formula could be applied:
							where:
							L	=	loading expressed as mg P per square metre lake surface in one year
								=	mean depth of lake in metres
							Tw	=	theoretical renewal time of lake water in years
							In other cases limit values of 0,2 mg/l for salmonid and of 0,4 mg/l for cyprinid waters, expressed as PO4, may be regarded as indicative in order to reduce eutrophication
7. Nitrites (mg/l NO2)	≤ 0,01		≤ 0,03		Molecular absorption spectrophotometry
8. Phenolic compounds (mg/l C6H5OH)		b		b	By taste		An examination by taste shall be made only where the presence of phenolic compounds is presumed
9. Petroleum hydrocarbons		c		c	Visual By taste	Monthly	A visual examination shall be made regularly once a month, with an examination by taste only where the presence of hydrocarbons is presumed
10. Non-ionised ammonia (mg/l NH3)	≤ 0,005	≤ 0,025	≤ 0,005	≤ 0,025	Molecular absorption spectrophotometry using indophenol blue or Nessler's method associated with pH and temperature determination	Monthly	Values for non-ionised ammonia may be exceeded in the form of minor peaks in the daytime
	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 the following:
11. Total ammonium (mg/l NH4)	≤ 0.04	≤ 1d	≤ 0.2	≤ 1d
12. Total residual chlorine (mg/l HOCl)		≤ 0,005		≤ 0,005	DPD-method (dietyl-p-phenylenediamene)	Monthly	The I-values correspond to pH = 6 Higher concentrations of total chlorine can be accepted if the pH is higher
13. Total zinc (mg/l Zn)		≤ 0,3		≤ 1,0	Atomic absorption spectrometry	Monthly	The I-values correspond to a water hardness of 100 mg/l CaCO3 For hardness levels between 10 and 500 mg/l corresponding limit values can be found in Annex II
14. Dissolved copper (mg/l Cu)	≤ 0,04		≤ 0,04		Atomic absorption spectrometry		The G-values correspond to a water hardness of 100 mg/l CaCO3 For hardness levels between 10 and 300 mg/l corresponding limit values can be found in Annex II

General observation: U.K.

It should be noted that the parametric values listed in this Annex assume that the other parameters, whether mentioned in this Annex or not, are favourable. This implies, in particular, that the concentrations of other harmful substances are very low. U.K.

Where two or more harmful substances are present in mixture, joint effects (additive, synergic or antagonistic effects) may be significant.

Abbreviations: U.K.

G

=

guide.

I

=

mandatory.

(0)

=

derogations are possible in accordance with Article 11.

ANNEX II U.K. PARTICULARS REGARDING TOTAL ZINC AND DISSOLVED COPPER

Total zinc (see Annex I, No 13, ‘Observations’ column) U.K.

Total zinc concentrations (mg/l Zn) for different water hardness values between 10 and 500 mg/l CaCO₃:

	Water hardness (mg/l CaCO3)
	10	50	100	500
Salmonid waters (mg/l Zn)	0,03	0,2	0,3	0,5
Cyprinid waters (mg/l Zn)	0,3	0,7	1,0	2,0

Dissolved copper (See Annex I, No 14, ‘Observations’ column) U.K.

Dissolved copper concentrations (mg/l Cu) for different water hardness values between 10 and 300 mg/l CaCO₃:

a The presence of fish in waters containing higher concentrations of copper may indicate a predominance of dissolved organo-cupric complexes.
	Water hardness (mg/l CaCO3)
	10	50	100	300
mg/l Cu	0,005a	0,022	0,04	0,112

ANNEX III U.K.

Part A U.K. Repealed Directive with its successive amendments

(referred to in Article 17)

a Directive 78/659/EEC has also been amended by the following unrepealed acts: the 1979 Act of Accession, the 1985 Act of Accession, the 1994 Act of Accession.
Council Directive 78/659/EEC (OJ L 222, 14.8.1978, p. 1)a
Council Directive 91/692/EEC (OJ L 377, 31.12.1991, p. 48)	Annex I, point (c) only
Council Regulation (EC) No 807/2003 (OJ L 122, 16.5.2003, p. 36)	Annex III, point 26 only

Part B U.K. List of time-limits for transposition into national law

(referred to in Article 17)

Directive	Time-limit for transposition
78/659/EEC	20 July 1980
91/692/EEC	1 January 1993

ANNEX IV U.K. CORRELATION TABLE

Directive 78/659/EEC	This Directive
Article 1(1) and (2)	Article 1(1) and (2)
Article 1(3), introductory phrase	Article 1(3), introductory phrase
Article 1(3), first indent	Article 1(3)(a)
Article 1(3), second indent	Article 1(3)(b)
Article 1(4), introductory phrase	Article 1(4), introductory phrase
Article 1(4), first indent	Article 1(4)(a)
Article 1(4), second indent	Article 1(4)(b)
Article 2(1)	Article 2, first subparagraph
Article 2(2)	Article 2, second subparagraph
Article 3	Article 3
Article 4(1) and (2)	Article 4(1)
Article 4(3)	Article 4(2)
Article 5	Article 5
Article 6(1), introductory phrase	Article 6(1), introductory phrase
Article 6(1), first indent	Article 6(1)(a)
Article 6(1), second indent	Article 6(1)(b)
Article 6(1), third indent	Article 6(1)(c)
Article 6(2)	Article 6(2)
Article 7	Article 7
Article 8	Article 8
Article 9	Article 9
Article 10	Article 10
Article 11	Article 11
Article 12	Article 12
Article 13(1) and Article 14	Article 13
Article 15, first subparagraph, introductory phrase	Article 14, first subparagraph, introductory phrase
Article 15, first subparagraph, first indent	Article 14, first subparagraph, point (a)
Article 15, first subparagraph, second indent	Article 14, first subparagraph, point (b)
Article 15, first subparagraph, third indent	Article 14, first subparagraph, point (c)
Article 15, first subparagraph, fourth indent	Article 14, first subparagraph, point (d)
Article 15, second subparagraph	Article 14, second subparagraph
Article 16	Article 15
Article 17(1)	—
Article 17(2)	Article 16
—	Article 17
—	Article 18
Article 18	Article 19
Annex I	Annex I
Annex II	Annex II
—	Annex III
—	Annex IV