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| DOE-STD-1128-98
Guide of Good Practices for Occupational Radiological Protection in Plutonium Facilities
Urinalysis. Urine sampling provides useful information about the amount of
plutonium excreted following an intake. After chemical isolation, the plutonium in
urine samples may be determined by various methods including: alpha
spectrometry (gas-flow proportional or surface-barrier detection), alpha counting
(zinc sulfide or liquid scintillation counting), fission track counting, and mass
spectrometry. Analytical procedures for in vitro measurement of plutonium and
other radionuclides have been published (Volchok and dePlanque, 1983; Gautier,
1983).
Urine samples should be collected away from the plutonium facility to minimize
cross-contamination. Samples should be collected in contamination-free
containers; measures should be considered for minimizing plateout on walls of
container surfaces (such as by addition of trace amounts of gold, oxalate, or nitric
acid).
plutonium and many other radioactive materials because more than half of the
material deposited in the upper respiratory tract is cleared rapidly to the stomach
and gastrointestinal (GI) tract.
The total fecal plus urinary elimination for the first few days after exposure,
combined with in vivo counts that might be obtained, may provide the earliest and
most accurate assessment of intake. Fecal samples taken during the second and
third day after an inhalation incident are likely to provide the most useful data
because the gastrointestinal hold-up time may vary from a few hours to a few days.
Fecal sampling is primarily a monitoring procedure for confirming and evaluating
suspected intakes, but is used at some plutonium facilities for routine periodic
monitoring as well. Workers may find fecal sampling unpleasant or objectionable,
and laboratory technicians may also have aversion to fecal sample analysis. Some
of these problems may be minimized if commercial fecal sample collection kits are
used for convenient collection and handling of samples (Fisher et al., 1982).
Collection kits also provide a means for collecting uncontaminated samples. Fecal
samples may require additional sample preparation before analysis.
5.4
ESTABLISHING BIOASSAY FREQUENCY
The bioassay measurement frequency should be based on 1) the potential risks of an intake
occurring and 2) the sensitivity of a bioassay program to detecting potential intakes. The bioassay
program sensitivity can be selected using specified intervals between measurements based on the
MDD associated with an interval.
5-15
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