Plutonium Biokinetics in Human Body A. Luciani - Kit-Bibliothek - FZK
Plutonium Biokinetics in Human Body A. Luciani - Kit-Bibliothek - FZK
Plutonium Biokinetics in Human Body A. Luciani - Kit-Bibliothek - FZK
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2.2 A DESCRIPTION OF THE UPDATED CONTAMINATION CASE<br />
The contam<strong>in</strong>ation <strong>in</strong>cident <strong>in</strong>vestigated <strong>in</strong> the present work is one of the best<br />
documented cases of a s<strong>in</strong>gle <strong>in</strong>take of transuranium elements worldwide ( 238 Pu, 239 Pu, 240 Pu,<br />
241 Pu, and 241 Am). This contam<strong>in</strong>ation case complies quite well the requirements previously<br />
described for us<strong>in</strong>g a data set of occupational exposure for model verification purposes.<br />
Furthermore it shows two important aspects:<br />
• The measurements carried out <strong>in</strong> recent years <strong>in</strong> occasion of dose assessments<br />
<strong>in</strong>tercomparisons showed a significant enhancement of <strong>Plutonium</strong> ur<strong>in</strong>ary excretion,<br />
particularly at long time after contam<strong>in</strong>ation. This was already po<strong>in</strong>ted out, but at a lesser<br />
extent, <strong>in</strong> other contam<strong>in</strong>ated subjects [122];<br />
• The <strong>Plutonium</strong> mixture <strong>in</strong>troduced by the subject conta<strong>in</strong>s 241 Am too, giv<strong>in</strong>g the<br />
possibility of carry<strong>in</strong>g out direct measurements of organs activity burden, otherwise<br />
hardly detectable <strong>in</strong> case of a contam<strong>in</strong>ation of pure <strong>Plutonium</strong>.<br />
For such characteristics it was already proposed as a case study <strong>in</strong> different<br />
<strong>in</strong>tercomparisons on dose assessment. It is present as “Case 8” <strong>in</strong> the IAEA <strong>in</strong>tercomparison<br />
[123] and it is the base for “Case 6” <strong>in</strong> the 3 rd European <strong>in</strong>tercomparison [124]. At the time of<br />
the <strong>in</strong>tercomparisons there was already a set of excretion and organ burden data from the first<br />
day after the <strong>in</strong>take up to almost ten years [125]. S<strong>in</strong>ce 1983 direct measurements of<br />
Americium burden <strong>in</strong> different organs were carried out also <strong>in</strong> Forschungszentrum Karlsruhe<br />
[126]. In the frame of the present work <strong>in</strong> 1999 a complete follow-up of this case was carried<br />
out <strong>in</strong> Forschungszentrum Karlsruhe and new data for the <strong>Plutonium</strong> and Americium amounts<br />
<strong>in</strong> bioassays (ur<strong>in</strong>e, feces and blood) and for the Americium organs burdens were obta<strong>in</strong>ed.<br />
The results of these direct and <strong>in</strong>direct measurements are extensively presented <strong>in</strong> the two<br />
paragraphs 2.3.3 and 2.4.3, respectively.<br />
2.2.1 THE CONTAMINATION EVENT<br />
The work<strong>in</strong>g area where the contam<strong>in</strong>ation event occurred was a radiochemical<br />
laboratory for the development of advanced nuclear fuel <strong>in</strong> a nuclear research centre. In the<br />
laboratory nuclear fuels microspheres had been produced <strong>in</strong> a glove box us<strong>in</strong>g a special<br />
gell<strong>in</strong>g technique. The waste water result<strong>in</strong>g from this technique was rout<strong>in</strong>eously collected<br />
and evaporated <strong>in</strong> the box. The residual waste water deriv<strong>in</strong>g from this process was<br />
transferred <strong>in</strong>to a second glove box for further evaporation and successive disposal.<br />
The subject (male, 26 years old at that time, 91 kg weight, 179 cm height) was<br />
work<strong>in</strong>g at the first glove box where the fuel microspehre were produced. On 24.05.83 at 4:15<br />
PM an explosion occurred <strong>in</strong> the second glove box dur<strong>in</strong>g the evaporation of three litres waste<br />
water as a consequence of a unexpected exothermic reaction. The subject left the laboratory<br />
immediately after the explosion, yet he resulted strongly contam<strong>in</strong>ated at face, hairs and<br />
clothes. He was immediately decontam<strong>in</strong>ated <strong>in</strong> the radiation protection unit of the research<br />
centre and nose swabs with bronchial slime samples were collected.<br />
In the glove boxes the wash<strong>in</strong>g water conta<strong>in</strong>ed <strong>Plutonium</strong> and Uranium <strong>in</strong> a mixture<br />
of hydroxide gel with 10 % of ammonium nitrate and about 3.5 % of hexamethylentetram<strong>in</strong>e.<br />
The α activity composition of the substance caus<strong>in</strong>g the <strong>in</strong>ternal contam<strong>in</strong>ation of the subject<br />
was 9 % 238 Pu, 55 % 239 Pu, 26% 240 Pu and 10 % 241 Am. The 241 Pu activity was 750 % of the<br />
total α activity. Size distribution analysis of dust samples collected <strong>in</strong> the laboratory was also<br />
carried out by means of scann<strong>in</strong>g electron microscope exposures and x ray analyses. The<br />
diameter of the particles conta<strong>in</strong><strong>in</strong>g <strong>Plutonium</strong> resulted to be between 3 and 40 µm.<br />
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