Council Directive 79/869/EEC of 9 October 1979 concerning the methods of measurement and frequencies of sampling and analysis of surface water intended for the abstraction of drinking water in the Member States
Modified by
  • Council Directive of 19 October 1981 (81/855/EEC), 31981L0855, November 7, 1981
  • Act of Accession of Spain and Portugal, 11985I, November 15, 1985
  • Council directive of 23 December 1991 (91/692/EEC), 31991L0692, December 31, 1991
  • Act of Accession of Austria, Sweden and Finland(adapted by Council Decision 95/1/EC of 1 January 1995), 11994N31995D0001, August 29, 1994
  • (adapted by Council Decision 95/1/EC of 1 January 1995), 31995D0001, January 1, 1995
  • Directive 2000/60/EC of the European Parliament and of the Councilof 23 October 2000establishing a framework for Community action in the field of water policy, 32000L0060, December 22, 2000
  • Council Regulation (EC) No 807/2003of 14 April 2003adapting to Decision 1999/468/EC the provisions relating to committees which assist the Commission in the exercise of its implementing powers laid down in Council instruments adopted in accordance with the consultation procedure (unanimity), 32003R0807, May 16, 2003
Council Directiveof 9 October 1979concerning the methods of measurement and frequencies of sampling and analysis of surface water intended for the abstraction of drinking water in the Member States(79/869/EEC) THE COUNCIL OF THE EUROPEAN COMMUNITIES,Having regard to the Treaty establishing the European Economic Community, and in particular Articles 100 and 235 thereof,Having regard to the proposal from the CommissionOJ No C 208, 1. 9. 1978, p. 2.,Having regard to the opinion of the European ParliamentOJ No C 67, 12. 3. 1979, p. 48.,Having regard to the opinion of the Economic and Social CommitteeOJ No C 128, 21. 5. 1979, p. 4.,Whereas the programme of action of the European Communities on the environmentOJ No C 112, 20. 12. 1973, p. 1. provides for the standardization or harmonization of the measuring methods used, so as to render the results of pollution measurements in the Community comparable;Whereas Council Directive 75/440/EEC of 16 June 1975 concerning the quality required of surface water intended for the abstraction of drinking water in the Member StatesOJ No L 194, 25. 7. 1975, p. 34., and in particular Article 5 (2) thereof, provides for adoption of a Community policy regarding the frequency of sampling and analysis of parameters, together with methods of measurement;Whereas any disparity between the provisions already applicable or in preparation in the various Member States concerning methods of measurement and the frequency of sampling and analysis for each parameter to determine the quality of surface water may create unequal conditions of competition and consequently directly affect the functioning of the common market; whereas it is therefore necessary to approximate the laws in this field, under Article 100 of the Treaty;Whereas it seems necessary for this approximation of laws to be accompanied by Community action designed to achieve through more comprehensive legislation one of the objectives of the Community in the sphere of protection of the environment and improvement of the quality of life; whereas certain specific provisions to this effect should therefore be laid down; whereas Article 235 of the Treaty should be invoked, as the powers required for this purpose have not been provided by the Treaty;Whereas, for the analyses carried out in the Member States, it is necessary to fix common reference methods of measurement to determine the values of the parameters defining the physical, chemical and microbiological characteristics of surface water intended for the abstraction of drinking water;Whereas, for the purpose of monitoring the required quality, it is necessary to take a regular minimum number of samples of surface water in order that the parameters specified in Annex II to Directive 75/440/EEC may be measured;Whereas the minimum frequency of sampling and analysis for each parameter should increase in proportion to the volume of water abstracted and the population served; whereas the frequency should increase with the degree of risk engendered by the deterioration of the quality of the water;Whereas technical and scientific progress may necessitate the rapid adjustment of some of the requirements defined in Annex I to this Directive, in order to take account, in particular, of alterations in the levels of the parameters specified in Annex II to Directive 75/440/EEC; whereas, in order to facilitate implementation of the necessary measures, a procedure should be laid down for establishing close collaboration between the Member States and the Commission in a Committee on Adaptation to Technical and Scientific Progress,HAS ADOPTED THIS DIRECTIVE:
Article 1This Directive concerns the reference methods of measurement and frequencies of sampling and analysis for the parameters listed in Annex II to Directive 75/440/EEC.
Article 2For the purposes of this Directive:"reference method of measurement" means the designation of a measurement principle or a succinct description of a procedure for determining the value of the parameters listed in Annex I to this Directive,"limit of detection" means the minimum value of the parameter examined which it is possible to detect,"precision" means the range within which 95% of the results of measurements made on a single sample, using the same method, are located,"accuracy" means the difference between the true value of the parameter examined and the average experimental value obtained.
Article 31.Analysis of samples of water taken shall concern those parameters set out in Annex II to Directive 75/440/EEC to which I and/or G values have been assigned.2.Member States shall as far as possible use the reference methods of measurement referred to in Annex I to this Directive.3.The values for the limit of detection and for the precision and accuracy of the methods of measurement used to check the parameters set out in Annex I to this Directive must be respected.
Article 41.The minimum annual frequencies of sampling and analysis for each parameter are set out in Annex II to this Directive. Sampling must as far as possible be spread over the year so as to give a representative picture of the quality of the water.2.Surface water samples must be representative of the quality of the water at the sampling point as defined in Article 5 (4) of Directive 75/440/EEC.
Article 5The containers used for samples, the agents or methods used to preserve part of a sample for the analysis of one or more parameters, the conveyance and storage of samples and the preparation of samples for analysis must not be such as to bring about any significant change in the results of the analysis.
Article 61.The competent authorities of the Member States shall fix frequencies of sampling and analysis for each parameter for each sampling point.2.The frequencies of sampling and analysis shall be not less than the minimum annual frequencies given in Annex II to this Directive.
Article 71.Where a survey by the competent authorities of surface water intended for the abstraction of drinking water shows that the values obtained for certain parameters are considerably superior to those set by the Member States in accordance with Annex II to Directive 75/440/EEC, the Member State concerned may reduce the frequency of sampling and analysis for these parameters.2.If there is no pollution in the cases referred to in paragraph 1 and if there is no risk of the quality of water deteriorating and if the water in question is superior in quality to the indications given in column A1 of Annex II to Directive 75/440/EEC, the authorities concerned may decide that no regular analysis is necessary.
Article 8At intervals of three years the Member States shall send information to the Commission on the implementation of this Directive, in the form of a sectoral report which shall also cover other pertinent Community Directives. This report shall be drawn up on the basis of a questionnaire or outline drafted by the Commission in accordance with the procedure laid down in Article 6 of Directive 91/692/EECOJ No L 377, 31. 12. 1991, p. 48. The questionaire (SIC! questionnaire) or outline shall be sent to the Member States six months before the start of the period covered by the report. The report shall be sent to the Commission within nine months of the end of the three-year period covered by it.The first report shall cover the period from 1993 to 1995 inclusive.The Commission shall publish a Community report on the implementation of the Directive within nine months of receiving the reports from the Member States.
Article 9To take account in particular of alterations in the levels of the parameters specified in Annex II to Directive 75/440/EEC, the amendments required to adapt:the reference methods of measurement set out in Annex I to this Directive,the limit of detection, the precision and the accuracy of these methods,the materials recommended for the containerto technical progress, shall be adopted in accordance with the procedure set out in Article 11 of this Directive.
Article 101.A Committee on Adaptation to Technical and Scientific Progress (hereinafter referred to as the "Committee"), consisting of representatives of the Member States and chaired by a Commission representative, is hereby set up for the purpose laid down in Article 9.2.The Committee shall draw up its rules of procedure.
Article 111.The Commission shall be assisted by the Committee on Adaptation to Technical and Scientific Progress.2.Where reference is made to this Article, Articles 5 and 7 of Decision 1999/468/ECOJ L 184, 17.7.1999, p. 23. shall apply.The period laid down in Article 5(6) of Decision 1999/468/EC shall be set at three months.3.The committee shall adopt its rules of procedure.
Article 121.Directive 75/440/EEC is hereby amended as follows:(a)Article 5 (2) shall be deleted;(b)in Article 5 (3) the words "those referred to in paragraph 2" shall be replaced by the words "the parametric values for the water quality in question".2.Paragraph 1 shall take effect within two years of the notification of this Directive.
Article 13The Member States shall bring into force the laws, regulations and administrative provisions necessary to comply with this Directive within two years of its notification. They shall forthwith inform the Commission thereof.
Article 14This Directive is addressed to the Member States.
nullANNEX IReference method of measuring the I and/or G values of the parameters in Council Directive 75/440/EEC
Surface water samples taken at the abstraction point are analysed and measured after sieving (wire mesh sieve) to remove any floating debris such as wood or plastic.For waters of Category A1, G value.For waters of Categories A2 and A3.For waters of Category A3.For waters of Categories A1, A2, and A3, I value.For waters of Categories A2, I value and A3.For waters of Categories A2 and A3, G value.Mixture of six standard substances all of the same concentration to be taken into consideration: fluoranthene; 3,4 benzofluoranthene: 11, 12-benzofluoranthene; 3, 4-benzopyrene; 1, 12-benzoperylene; indano /1, 2, 3 - cd/pyrene.Mixture of three substances all of the same concentration to be taken into consideration: parathion, hexachlorocyclohexane, dieldrin.If the samples contain so much suspended matter as to require special preliminary treatment, the accuracy values shown in column E in this Annex may as an exception be exceeded and will be regarded as a target. These samples must be treated so as to ensure that the analysis covers the largest quantity of substances to be measured.As this method is not in current use in all the Member States, it is not certain that the limit of detection required for checking the values in Directive 75/440/EEC can be attained.Absence in 5000 ml (A1, G) and absence in 1000 ml (A2, G).
ParameterLimit of detectionPrecision±Accuracy±Reference method of measurementMaterials recommended for the container
(A)(B)(C)(D)(E)(F)(G)
1pHpH unit0·10·2ElectrometryMeasured in situ at the time of sampling without prior treatment of the sample
2Coloration (after simple filtration)mg Pt/l510 %20 %Filtering through a glass fibre membranePhotometric method using the platinumcobalt scale
3Total suspended solidsmg/l5 %10 %Filtering through a 0·45 μm filter membrane, drying at 105 °C and weighing
Centrifuging (for at least 5 mins with mean acceleration of 2800 to 3200 g), drying at 105 °C and weighing
4Temperature°C0·51ThermometryMeasured in situ at the time of sampling without prior treatment of the sample
5Conductivity at 20 °CμS/cm5 %10 %Electrometry
6OdourDilution factor at 25 °CBy successive dilutionsGlass
7Nitratesmg/l NO3210 %20 %Molecular absorption spectrophotometry
8Fluoridesmg/l F0·0510 %20 %Molecular absorption spectrophotometry after distillation if necessary
Ion selective electrodes
9Total extractable organic chlorinemg/l Cl
10Dissolved ironmg/l Fe0·0210 %20 %Atomic absorption spectrophotometry after filtering through a filter membrane (0·45 μm)
Molecular absorption spectrophotometry after filtering through a 0·45 μm filter membrane
11Manganesemg/l Mn0·0110 %20 %Atomic absorption spectrophotometry
0·0210 %20 %Atomic absorption spectrophotometry
Molecular absorption spectrophotometry
12Coppermg/l Cu0·00510 %20 %Atomic absorption spectrophotometry
Polarography
0·0210 %20 %Atomic absorption spectrophotometry
Molecular absorption spectrophotometry
Polarography
13Zincmg/l Zn0·0110 %20 %Atomic absorption spectrophotometry
0·0210 %20 %Atomic absorption spectrophotometry
Molecular absorption spectrophotometry
14Boronmg/l B0·110 %20 %Molecular absorption spectrophotometryMaterials not containing boron in any significant quantities
Atomic absorption spectrophotometry
15Berylliummg/l Be
16Cobaltmg/l Co
17Nickelmg/l Ni
18Vanadiummg/l V
19Arsenicmg/l As0·00220 %20 %Atomic absorption spectrophotometry
0·01Atomic absorption spectrophotometry
Molecular absorption spectrophotometry
20Cadmiummg/l Cd0·000230 %30 %Atomic absorption spectrophotometry
0·001Polarography
21Total chromiummg/l Cr0·0120 %30 %Atomic absorption spectrophotometry
Molecular absorption spectrophotometry
22Leadmg/l Pb0·0120 %30 %Atomic absorption spectrophotometry
Polarography
23Seleniummg/l Se0·005Atomic absorption spectrophotometry
24Mercurymg/l Hg0·00010·000230 %30 %Flameless atomic absorption spectrophotometry (cold vaporization)
25Bariummg/l Ba0·0215 %30 %Atomic absorption spectrophotometry
26Cyanidemg/l CN0·0120 %30 %Molecular absorption spectrophotometry
27Sulphatesmg/l SO41010 %10 %Gravimetric analysis
EDTA compleximetry
Molecular absorption spectrophotometry
28Chloridesmg/l Cl1010 %10 %Titration (Mohr's method)
Molecular absorption spectrophotometry
29Surfactants (reacting with methylene blue)mg/l (Lauryl Sulphate)0·0520 %Molecular absorption spectrophotometry
30Phosphatesmg/l P2O50·0210 %20 %Molecular absorption spectrophotometry
31Phenols (phenol index)mg/l C6H5OH0·00050,00050,0005Molecular absorption spectrophotometry 4 amionoantipyrine methodGlass
0·00130 %50 %Paranitraniline method
32Dissolved or emulsified hydrocarbonsmg/l0·0120 %30 %Infra-red spectrometry after extraction by carbon tetrachlorideGlass
0·04Gravimetry after extraction by petroleum ether
33Polycyclic aromatic hydrocarbonsmg/l0·0000450 %50 %Measurement of fluorescence in the UV after thin layer chromatographyComparative measurement in relation to a mixture of six control substances with the same concentrationGlass or aluminiumGlass or aluminium
34Total pesticides (parathion, hexachlorocyclohexane, dieldrin)mg/l0·000150 %50 %Gas or liquid chromatography after extraction by suitable solvents and purificationIdentification of the constituents of the mixtureQuantitative analysisGlass
35Chemical oxygen demand (COD)mg/l O21520 %20 %Potassium dichromate method
36Dissolved oxygen saturation rate%510 %10 %Winkler's methodGlass
Electrochemical method
37Biochemical oxygen demand (BOD5) at 20 °C without nitrificationmg/l O221,52Determination of dissolved oxygen before and after five-day incubation at 20 °C ± 1 °C, in complete darkness Addition of a nitrification inhibitor
38Nitrogen by Kjeldahl method (except in NO2 and NO3)mg/l N0·50,50,5Mineralization, distillation by Kjeldahl method and ammonium determination by means of molecular absorption spectrophotometry or titration
39Ammoniummg/l NH40·010·10,0310 %0,0320 %Molecular absorption spectrophotometry
40Substances extractable with chloroformmg/lExtraction at neutral pH value by purified chloroform, evaporation in vacuo at room temperature, weighing of residue
41Total organic carbonmg/l C
42Residual organic carbon after flocculation and membrane filtration (5 μm)mg/l C
43Total coliforms/100 ml5500Culture at 37 °C on an appropriate specific solid medium (such as Tergitol lactose agar, Endo agar, 0·4 % Teepol broth) with filtration or without filtration and colony count. Samples must be diluted or, where appropriate, concentrated in such a way as to contain between 20 and 100 colonies. If necessary, identification by gasification.Sterilized glass
5500Method of dilution with fermentation liquid substrates in at least three tubes in three dilutions. Sub-culturing of the positive tubes on a confirmation medium. Count according to MPN (most probable number). Incubation temperature: 37 °C ± 1 °C.
44Faecal coliforms/100 ml2200Culture at 44 °C on an appropriate specific solid medium (such as Tergitol lactose agar, Endo agar, 0·4 % Teepol broth) with filtration or without filtration and colony count. Samples must be diluted or, where appropriate, concentrated in such a way as to contain between 10 and 100 colonies. If necessary, identification by gasification.Sterilized glass
2200Method of dilution with fermentation in liquid substrates in at least three tubes in three dilutions. Sub-culturing of the positive tubes on a confirmation medium. Count according to MPN (most probable number). Incubation temperature 44 °C ± 0.5 °C.
45Faecal streptococci/100 ml2200Culture at 37 °C on an appropriate solid medium (such as sodium azide) with filtration or without filtration and colony count. Samples must be diluted or, where appropriate, concentrated in such a way as to contain between 10 and 100 colonies.Sterilized glass
2200Method of dilution in sodium azide broth in at least three tubes with three dilutions. Count according to MPN (most probable number)
46Salmonella1/5000 ml1/1000 mlConcentraion by filtration (on membrane or appropriate filter).Sterilized glass
Innoculation into pre-enrichment medium. Enrichment and transfer into isolating gelese — Identification.
ANNEX IIMinimum annual frequency of sampling and analysis for each parameter in Directive 75/440/EEC
Quality of surface waters, Annex II Directive 75/440/EEC.Classification of parameters according to frequency.Frequency to be determined by the competent national authorities.Assuming that such surface water is intended for the abstraction of drinking water, the Member States are recommended to carry out at least annual sampling of this category of water (A3, III, ≤ 10000).
Population servedA1A2A3
IIIIIIIIIIIIIIIIII
10000
> 10000 to ≤ 300001121311
> 30000 to ≤ 10000021421621
> 100000328411241
CATEGORIES
IIIIII
ParameterParameterParameter
1pH10Dissolved iron8Fluorides
2Coloration11Manganese14Boron
3Total suspended solids12Copper19Arsenic
4Temperature13Zinc20Cadmium
5Conductivity27Sulphates21Total chromium
6Odour29Surfactants22Lead
7Nitrates31Phenols23Selenium
28Chlorides38Nitrogen by Kjeldahl method24Mercury
30Phosphates43Total coliforms25Barium
35Chemical oxygen demand (COD)44Faecal coliforms26Cyanide
36Dissolved oxygen saturation rate32Dissolved or emulsified hydrocarbons
37Biochemical oxygen demand (BOD5)33Polycyclic aromatic hydrocarbons
39Ammonium34Total pesticides
40Substances extractables with chloroform
45Faecal streptococci
46Salmonella