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 />
Subsequent reports in the series present radionuclide-specific information for the<br />
design and planning <strong>of</strong> monitoring programmes and retrospective assessment <strong>of</strong><br />
occupational internal doses.<br />
(9) The material presented in this report series is not intended for applications<br />
beyond the scope <strong>of</strong> occupational radiation protection. An example <strong>of</strong> such an<br />
application is the assessment <strong>of</strong> a case <strong>of</strong> substantial radionuclide intake, where organ<br />
doses can approach or exceed the thresholds for tissue reactions, and where medical<br />
treatment may require an individual-specific reconstruction <strong>of</strong> the magnitude <strong>of</strong><br />
absorbed doses and associated parameters characterising the exposure.<br />
1.2 Protection quantities and dose coefficients in this report series<br />
(10) The protection quantities defined by <strong>ICRP</strong>, equivalent dose and effective dose,<br />
are fundamental to the application <strong>of</strong> <strong>ICRP</strong> recommendations. The concept <strong>of</strong><br />
effective dose provides a single quantity that may be used to characterise both internal<br />
and external individual exposures in a manner that is independent <strong>of</strong> the individual’s<br />
body-related parameters, such as sex, age (for adults), anatomy, physiology and race.<br />
In order to achieve wide applicability, the protection quantities (effective dose and<br />
equivalent dose) are defined using computational models with broad averaging <strong>of</strong><br />
physiological parameter values. Specifically, Publication 89 (<strong>ICRP</strong> 1975, 2002)<br />
defines the key parameters <strong>of</strong> the Reference Individuals (the mass, geometry and<br />
composition <strong>of</strong> human organs and tissues), while this report series provides relevant<br />
parameters for the Reference Worker (<strong>ICRP</strong> 1994) together with an associated set <strong>of</strong><br />
<strong>ICRP</strong> reference biokinetic models.<br />
(11) Effective dose is not an individual-specific dose quantity, but rather the dose<br />
to a Reference Person under specified exposure conditions. In the general case, the<br />
Reference Person can be either a Reference Worker (see Glossary) or a Reference<br />
Member <strong>of</strong> the Public <strong>of</strong> a specified age.<br />
(12) The protection quantities for internal exposure (committed effective dose and<br />
committed equivalent dose) are derived using models and are not directly measurable.<br />
For retrospective assessments <strong>of</strong> internal exposure, the dose can be assessed from<br />
measurements <strong>of</strong> the amounts <strong>of</strong> radionuclides in the human body, their rates <strong>of</strong><br />
excretion or their concentrations in the ambient air. In contrast, the operational<br />
quantities for exposure to external radiation fields are directly measurable.<br />
(13) The dose coefficients and dose per unit content values presented in this report<br />
series are given for a Reference Worker with an average breathing rate <strong>of</strong> 1.2 m 3 h -1<br />
during an 8 h working day.. These data are provided for a range <strong>of</strong> physico-chemical<br />
forms for each radionuclide and for a range <strong>of</strong> aerosol particle size distributions. Data<br />
for ingestion and injection (i.e. direct entry to the blood) are provided to allow the<br />
interpretation <strong>of</strong> bioassay data for cases <strong>of</strong> inadvertent ingestion (e.g. <strong>of</strong> material on<br />
contaminated skin) or rapid absorption through intact or damaged skin (injection).<br />
(14) While the generic definition <strong>of</strong> protection quantities remains unchanged in the<br />
most recent recommendations (<strong>ICRP</strong>, 2007), there have been changes that affect<br />
calculated values <strong>of</strong> dose per unit radiation exposure, including changes to radiation<br />
and tissue weighting factors, adoption <strong>of</strong> reference computational phantoms (<strong>ICRP</strong>,<br />
2009), and the development <strong>of</strong> the new generation <strong>of</strong> reference biokinetic models.<br />
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