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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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2.4.2.2 Performances<br />

The energy calibration of the alpha detectors was carried out us<strong>in</strong>g standard sources<br />

conta<strong>in</strong><strong>in</strong>g 233 U, 239 Pu, 241 Am and 244 Cm. The FWHM of the detectors used <strong>in</strong> the laboratory is<br />

about 17 keV for 241 Am (energy resolution about 0.3 %). In the practical situations the FWHM<br />

and therefore the energy resolution depend on the thickness of the deposit on the planchet: 30-<br />

35 keV may be considered as an <strong>in</strong>dicative value of FWHM for most of the actual<br />

measurement conditions [151].<br />

At the present the rout<strong>in</strong>e measurements performed at the <strong>FZK</strong> Toxicological<br />

Laboratory are not able to discrim<strong>in</strong>ate 239 Pu from 240 Pu. Thus, efficiency factors and,<br />

consequently, activity measurements on such radioisotopes relate to the sum of their<br />

contributions.<br />

Efficiency calibration is normally carried out us<strong>in</strong>g standard sources of 241 Am of 523<br />

Bq activity certified at 14.7.1989.<br />

The <strong>FZK</strong> Toxicological Laboratory provides a value of 5•10 -4 Bq for the MDA for<br />

each radionuclide. The value refers to the whole bioassay laboratory equipped with numerous<br />

alpha spectrometric cha<strong>in</strong>s: therefore it can be considered as an <strong>in</strong>dication of the general<br />

performances of the laboratory.<br />

2.4.2.3 Measurements execution<br />

A blood sample was taken from the subject <strong>in</strong> the period of stay<strong>in</strong>g <strong>in</strong> the<br />

Forschungszentrum Karlsruhe. Three ur<strong>in</strong>e and feces samples were collected by the subject<br />

himself <strong>in</strong> the follow<strong>in</strong>g days after the return to his residence town. Therefore he was<br />

provided with the proper vials and <strong>in</strong>structed on how to handle them. The samples were sent<br />

by post to Forschungszentrum Karlsruhe. The sample collection protocol was set <strong>in</strong> order to<br />

collect samples relat<strong>in</strong>g to the whole excretion.<br />

As the samples were received, they were undergone to chemical preparation <strong>in</strong> order<br />

to detect isotopes of <strong>Plutonium</strong> and Americium. Therefore for each collected sample the<br />

separation procedure has provided two further samples, accord<strong>in</strong>g to the block diagram of<br />

Figure 2.4.1: one conta<strong>in</strong><strong>in</strong>g <strong>Plutonium</strong> isotopes, and the other one conta<strong>in</strong><strong>in</strong>g Americium.<br />

On these samples alpha spectrometry was carried out by <strong>in</strong>clud<strong>in</strong>g them <strong>in</strong> the rout<strong>in</strong>e<br />

measurement programme daily carried out by the <strong>FZK</strong> Toxicological Laboratory on samples<br />

from the occupationally exposed workers.<br />

2.4.3 RESULTS OF THE MEASUREMENTS<br />

The results of the measurements for the collected blood, ur<strong>in</strong>e and feces samples are<br />

given <strong>in</strong> Table 2.4.1 [151]. As previously stated the activity measurements on 239 Pu and 240 Pu<br />

radioisotopes relate to the sum of their contributions. The activity <strong>in</strong> blood samples resulted<br />

lower then the MDA for 238 Pu and 241 Am. For all the other k<strong>in</strong>d of measurements ( 239 Pu+ 240 Pu<br />

<strong>in</strong> blood and any radioisotopes <strong>in</strong> ur<strong>in</strong>e and feces samples) the activity values resulted to be<br />

higher than the MDA.<br />

79

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