This is the original version (as it was originally made).
Regulation 5
Regulation 6A
| Parameters | Maximum concentration or value | Units of measurement | |
|---|---|---|---|
(i) Enforcement action by the Welsh Ministers is deemed justified on radiological protection grounds without further consideration where radon concentrations exceed 1,000 Bq/1. | |||
(ii) If tritium concentration exceeds its parametric value, an investigation (which may include analysis) of the presence of artificial radionuclides must be carried out.” | |||
| Indicative dose (for radioactivity) | 0,10 | mSv | |
| Radon(i) | 100 | Bq/1 | |
| Tritium (for radioactivity)(ii) | 100 | Bq/l | |
Regulation 7
Regulation 6A
1.—(1) In relation to the radon parameter in the radioactive substances parameters table, a water undertaker—
(a)must ensure that a representative survey is carried out in accordance with sub-paragraph (2) to determine the likelihood of a supply failing to comply with the relevant parametric concentration or value specified in the radioactive substances parameters table; and
(b)must carry out monitoring where there is reason to believe, on the basis of the results of the representative surveys or other reliable information, including any risk assessment carried out in accordance with regulation 28, that the parametric value for the radon parameter laid down in the radioactive substances parameters table might be exceeded.
(2) A representative survey must be designed in such a way—
(a)as to be capable of determining the scale and nature of likely exposure to radon in water intended for human consumption originating from different types of groundwater sources and wells in different geological areas; and
(b)that underlying parameters, especially the geology and hydrology of the area, radioactivity of rock or soil, and well type, can be identified and used to direct further action to areas of likely high exposure.
2.—(1) In relation to the tritium parameter in the radioactive substances parameters table, a water undertaker—
(a)must carry out monitoring where an anthropogenic source of tritium or other artificial radionuclides is present within a water supply zone and it cannot be shown on the basis of other surveillance programmes or investigations, including any risk assessment carried out in accordance with regulation 28, that the level of tritium is below the parametric value listed in the radioactive substances parameters table; and
(b)must carry out an investigation of the presence of other artificial radionuclides if the concentration of tritium exceeds the parametric value listed in the radioactive substances parameters table.
(2) Where monitoring is required by sub-paragraph (1) samples must be taken in accordance with regulation 9(1) and (3).
3.—(1) In relation to the indicative dose (“ID”) parameter in the radioactive substances parameters table, a water undertaker must carry out monitoring where a source of artificial radioactivity or elevated natural radioactivity is present in a water supply zone and it cannot be shown on the basis of other surveillance programmes or investigations, including any risk assessment carried out in accordance with regulation 28, that the level of ID is below the parametric value listed the radioactive substances parameters table.
(2) Where monitoring is required by sub-paragraph (1) in relation to artificial radionuclides samples must be taken in accordance with regulation 9(1) and (3).
(3) Where monitoring is required by sub-paragraph (1) in relation to a source of elevated natural radioactivity—
(a)the Welsh Ministers must specify, by notice in writing to the water undertaker, the frequency of the monitoring required of—
(i)gross alpha activity;
(ii)gross beta activity; or
(iii)individual natural radionuclides,
depending on the screening strategy adopted by the water undertaker pursuant to Schedule 5; and
(b)the frequency of monitoring required under sub-paragraph (a) may vary from a single check measurement to the frequencies required for sampling in accordance with regulation 9(1).
(4) Where a single check for natural radioactivity is specified under paragraph (3)(a), the water undertaker must carry out a further check if any change occurs in relation to the supply which is likely to influence the concentrations of radionuclides in the supply.
4. Where treatment to reduce the level of radionuclides in a water supply zone has been undertaken, to verify the continued efficacy of that treatment, the water undertaker must—
(a)monitor the supply for total indicative dose, radon and tritium in accordance the provisions of this Schedule; and
(b)take samples in accordance with regulation 9(1) and (3).
5. Where a parametric value in the radioactive substances parameters table is exceeded in relation to a particular sample taken by a water undertaker, the Welsh Ministers must specify, by notice in writing to the water undertaker, the extent of resampling necessary to ensure that the measured values are representative of an average activity concentration for a full year.”
Regulation 8
Regulation 6A
1. A water undertaker may use reliable screening strategies to indicate the presence of radioactivity in water intended for human consumption.
2. The strategies referred to in paragraph 1 may include screening for–
(a)certain radionuclides or individual radionuclide; or
(b)gross alpha activity or gross beta activity (where appropriate gross beta activity may be replaced by residual beta activity after subtraction of the K-40 activity concentration).
3. If one of the activity concentrations exceeds 20% of the corresponding derived value or the tritium concentration exceeds its parametric value listed in Schedule 2A an analysis of additional radionuclides is required.
4. A water undertaker must, in deciding which radionuclides require to be measured for each supply, take into account all relevant information about likely sources of radioactivity.
5. Subject to paragraph 6 the recommended screening values are–
(a)0,1Bq/l for gross alpha activity; and
(b)1,0Bq/l for gross beta activity.
6. If the gross alpha activity exceeds 0,1Bq/l or the gross beta activity exceeds 1,0Bq/l, analysis for specific radionuclides is required.
7. The Welsh Ministers may set alternative screening levels for gross alpha activity and gross beta activity where it can be demonstrated by the water undertaker that the alternative levels are in compliance with an indicative dose of 0,1 mSv.
8. The radionuclides to be measured must be based on all relevant information about likely sources of radioactivity.
9. The indicative dose must be calculated from–
(a)the measured radionuclide concentrations and the dose coefficients laid down in Annex III, Table A of Directive 96/29/Euratom(1); or
(b)more recent information recognised by the Welsh Ministers, on the basis of the annual intake of water (730 1 for adults).
10. Where the following formula is satisfied, it can be assumed that the indicative dose is less than the parametric value of 0,1 mSv and no further investigation is required–
where:
Ci(obs) = observed concentration of radionuclide i
Ci(der) = derived concentration of radionuclide i
n = number of radionuclides detected.
| Origin | Nuclide | Derived concentration |
|---|---|---|
(1) This table includes values for the most common natural and artificial radionuclides; these are precise values, calculated for a dose of 0,1 mSV, an annual intake of 730 litre and using the dose coefficients laid down in Annex III, Table A of Directive 96/29/ Euratom; derived concentrations for other radionuclides can be calculated on the same basis, and values can be updated on the basis of more recent information recognised by the Welsh Ministers. | ||
(2) This table allows only for the radiological properties of uranium, not for its chemical toxicity. | ||
| Natural | U-238(2) | 3,0 Bq/1 |
U-234(2) | 2,8 Bq/1 | |
Ra-226 | 0,5 Bq/1 | |
Ra-228 | 0,2 Bq/1 | |
Pb-210 | 0,2 Bq/1 | |
Po-210 | 0,1 Bq/1 | |
| Artificial | C-14 | 240 Bq/1 |
Sr-90 | 4,9 Bq/1 | |
Pu-239/Pu-240 | 0,6 Bq/1 | |
Am-241 | 0,7 Bq/1 | |
Co-60 | 40 Bq/1 | |
Cs-134 | 7,2 Bq/1 | |
Cs-137 | 11 Bq/1 | |
1-131 | 6,2 Bq/1 | |
11. For the following parameters and radionuclides, the method of analysis used must, as a minimum, be capable of measuring activity concentrations with a limit of detection specified below:
| Parameters and radionuclides | Limit of detection (Notes 1,2) | Notes |
|---|---|---|
Tritium | 10 Bq/1 | Note 3 |
Radon | 10 Bq/1 | Note 3 |
gross alpha | 0,04 Bq/1 | Note 4 |
gross beta | 0,4 Bq/1 | Note 4 |
U-238 | 0,02 Bq/1 | |
U-234 | 0,02 Bq/1 | |
Ra-226 | 0,04 Bq/1 | |
Ra-228 | 0,02 Bq/1 | Note 5 |
Pb-210 | 0,02 Bq/1 | |
Po-210 | 0,01 Bq/1 | |
C-14 | 20 Bq/1 | |
Sr-90 | 0,4 Bq/1 | |
Pu-239/Pu-240 | 0,04 Bq/1 | |
Am-241 | 0,06 Bq/1 | |
Co-60 | 0,5 Bq/1 | |
Cs-134 | 0,5 Bq/1 | |
Cs-137 | 0,5 Bq/1 | |
I-131 | 0,5 Bq/1 |
Note 1: The limit of detection must be calculated according to the ISO standard 11929: Determination of the characteristic limits (decision threshold, detection limit, and limits of confidence interval) for measurements of ionising radiation – Fundamentals and application, with probabilities of errors of 1st and 2nd kind of 0,05 each.
Note 2: Measurement uncertainties must be calculated and reported as complete standard uncertainties, or as expanded uncertainties with an expansion factor of 1,96 according the ISO Guide for the Expression of Uncertainty in Measurement.
Note 3: The limit of detection for tritium and for radon is 10% of its parametric value of 100 Bq/1.
Note 4: The limit of detection for gross alpha activity and gross beta activities are 40% of the screening values of 0,1 and 1,0 Bq/1 respectively.
Note 5: This limit of detection applies only to initial screening for indicative dose for a new water source; if initial checking indicates that it is not plausible that Ra-228 exceeds 20% of the derived concentration, the limit of detection may be increased to 0,08 Bq/1 for routine Ra-228 nuclide specific measurements, until a subsequent re-check is required.”
OJ No. L 159, 29.6.1996, p. 1.
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