Occupational Intakes of Radionuclides Part 1 - ICRP
Occupational Intakes of Radionuclides Part 1 - ICRP
Occupational Intakes of Radionuclides Part 1 - ICRP
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DRAFT REPORT FOR CONSULTATION<br />
chronic intakes are not given in this publication, but equilibrium values <strong>of</strong> bioassay<br />
quantities for continuous chronic exposure are provided for some radionuclides.<br />
6.4.5 Influence <strong>of</strong> decorporation therapy<br />
(349) In cases involving internal contamination, blocking, dilution, or chelating<br />
agents may be used to enhance the clearance <strong>of</strong> the activity from the body and reduce<br />
committed doses. The use <strong>of</strong> interventional techniques to enhance the body’s natural<br />
elimination rate <strong>of</strong> the compound, or possibly to block the uptake <strong>of</strong> the radionuclide<br />
in sites where high uptake may occur (e.g., radioiodine in the thyroid), may partially<br />
or completely invalidate the use <strong>of</strong> standardized model approaches described above to<br />
estimate the intake and dose (NCRP, 2009).<br />
(350) The use <strong>of</strong> chelating agents such as DTPA, for example, may influence<br />
excretion rates for weeks or months after cessation <strong>of</strong> treatment.<br />
(351) It is not feasible to give specific advice as the treatment <strong>of</strong> any bioassay data<br />
depends upon the circumstances <strong>of</strong> the exposure and the need and timescale required<br />
for the dose assessment.<br />
6.4.6 Wounds<br />
(352) Because <strong>of</strong> their nature, intakes <strong>of</strong> radionuclides resulting from contaminated<br />
cuts or wounds typically account for an appreciable proportion <strong>of</strong> high dose<br />
exposures. <strong>Radionuclides</strong> may be transferred from the wound site to blood and to<br />
other organs and tissues, and the NCRP has developed a model to describe this<br />
transfer for various chemical forms <strong>of</strong> selected radionuclides (NCRP, 2007). Coupled<br />
with an element-specific systemic biokinetic model, the NCRP model can be used to<br />
calculate committed doses to organs and tissues and committed effective doses<br />
following transfer <strong>of</strong> the radionuclide to the blood and systemic circulation, as well as<br />
to predict urinary and faecal excretion.<br />
(353) As noted in Section 3.1, the assessment <strong>of</strong> internal contamination resulting<br />
from wounds is in practice treated on a case-by-case basis using expert judgement. In<br />
many cases, the amount <strong>of</strong> a radionuclide transferred from a wound site to blood may<br />
be assessed directly from urine bioassay data. Section 3.4 summarises the main<br />
features <strong>of</strong> the NCRP model, since this information may be <strong>of</strong> use in the interpretation<br />
<strong>of</strong> bioassay data for individual cases <strong>of</strong> wound contamination.<br />
6.5 Uncertainties in Internal Dose Assessment Based on Bioassay<br />
(354) Publication 103 (<strong>ICRP</strong>, 2007) makes the following statement with respect to<br />
the assessment <strong>of</strong> uncertainties:<br />
In order to assess radiation doses, models are necessary to simulate the<br />
geometry <strong>of</strong> the external exposure, the biokinetics <strong>of</strong> incorporated<br />
radionuclides, and the human body. The reference models and necessary<br />
reference parameter values are established and selected from a range <strong>of</strong><br />
experimental investigations and human studies through judgements. For<br />
regulatory purposes, these models and parameter values are fixed by<br />
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