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Safety_Series_041_1975 - gnssn - International Atomic Energy ...

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Please see http://www.ns-iaea.org/standards/<br />

42 APPENDIX I<br />

maintained. The la b ora tories should maintain uniform m inim um<br />

detectable le v e l capabilities and should routinely take part in in te r­<br />

laboratory quality con trol p rogra m m es. A minimum quality con trol<br />

frequency of 10% o f all nuclide analysis, including in-house blanks,<br />

standards and splits is recom m ended.<br />

A nalytical con trol m ethods generally include cro ss-ch e ck in g<br />

or splitting sam ples with a con trol laboratory. A c r o s s -c h e c k<br />

involves the analyses o f sam ples provided by the con trol laboratory<br />

and com parison o f the resu lts with those of the con trol laboratory<br />

as w ell as with other la b ora tories that receiv ed portions of the sam e<br />

sam ples. Splitting a sam ple involves obtaining two iden tical sam ples<br />

from a single collection , one sam ple being, analysed by the m on i­<br />

toring laboratory and the other by the con trol la b oratory, with<br />

subsequent com p arison of resu lts. When splitting sam ples for<br />

interlaboratory com p a rison , it is very im portant that both sam ples<br />

parts are represen tative of the m edia in question.<br />

Some typical analytical m ethods and the associated detection<br />

capabilities are illu strated in Tables I and II.<br />

REPORTING PROCEDURES<br />

R eporting of data should be done follow ing a clea r and uniform<br />

form at suitable for autom atic data p rocessin g . '<br />

The reported inform ation should generally include the follow ing<br />

inform ation:<br />

(1) G eographic location of sam ple site<br />

(2) Sample type (m edia)<br />

(3) Sample num ber (optional)<br />

(4) Identification o r organization o r person collecting the sample<br />

(5) Identification of organization analysing the sam ple<br />

(6) Tim e and date sam ple was taken (include duration of sam ple<br />

period for integrated sam ples)<br />

(7) Sample preparation as appropriate (e. g. concentration or<br />

wet versu s dry)<br />

(8) Type o f analysis p erform ed<br />

(9) Value and units for each analysis and associated 2-sigm a<br />

e rro r<br />

(10) P aram eters needed to calculate decay of sam ple p rio r to<br />

analysis where sh ort-liv ed radionuclides are involved<br />

(11) Any known events that may have affected the analytical<br />

resu lts.<br />

Much o f the above inform ation, such as sam ple site location and<br />

organization iden tification , can be coded to reduce the re co rd volum e.

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