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Plutonium Biokinetics in Human Body A. Luciani - Kit-Bibliothek - FZK

Plutonium Biokinetics in Human Body A. Luciani - Kit-Bibliothek - FZK

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L A is the air layer <strong>in</strong> µgcm -2 ;<br />

P is the pressure with<strong>in</strong> the vacuum chamber <strong>in</strong> Torr<br />

d is the source-detector spac<strong>in</strong>g <strong>in</strong> cm.<br />

The recoil contam<strong>in</strong>ation is one of the ma<strong>in</strong> factors affect<strong>in</strong>g the background radioactivity <strong>in</strong><br />

the vacuum chamber. Therefore it particularly <strong>in</strong>fluences performances of alpha spectrometry<br />

systems <strong>in</strong> terms of m<strong>in</strong>imum detectable activity. Another factor that plays an important role<br />

specifically for the alpha spectrometry systems is the chemical yield <strong>in</strong> the preparation and<br />

separation process. A specific guidel<strong>in</strong>e gives the suitable expressions for calculat<strong>in</strong>g the<br />

MDA [150] but the general considerations previously <strong>in</strong>troduced are still valid.<br />

At the end of the alpha spectrometry measurement, the radionuclide activity <strong>in</strong> the<br />

sample is calculated us<strong>in</strong>g the tracer yield (Y T) given by:<br />

where:<br />

T<br />

Nn is the net area for the peak of tracer alpha;<br />

tM is the measurement time;<br />

εT is the efficiency factor for the tracer;<br />

AT is the tracer activity added at the beg<strong>in</strong>n<strong>in</strong>g of the sample manipulation.<br />

76<br />

equation 2.4.3<br />

The activity of the radionuclide of <strong>in</strong>terest (A R) <strong>in</strong> the sample is f<strong>in</strong>ally evaluated as<br />

follows:<br />

where:<br />

R<br />

Nn is the net area for the peak of the radionuclide of <strong>in</strong>terest;<br />

tM is the measurement time;<br />

YT is the tracer yield (from equation 2.4.3)<br />

εR is the efficiency factor for the radionuclide of <strong>in</strong>terest.<br />

2.4.2 MATERIALS AND METHODS<br />

2.4.2.1 Description of the devices<br />

A R = N n<br />

R<br />

t Mε RY T<br />

YT = N T<br />

n<br />

tMε T AT equation 2.4.4<br />

The ur<strong>in</strong>e samples were collected <strong>in</strong> a vial 2 litres volume. The feces were collected <strong>in</strong><br />

two vials: the first used just as transport conta<strong>in</strong>er (1 litre volume); It conta<strong>in</strong>s the second<br />

smaller vial (0.5 litre volume) with excreta <strong>in</strong>side. This second vial is ashed together with the<br />

excreta dur<strong>in</strong>g the chemical preparation of the sample. Samples of 100 millilitre volume were

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