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DOE-STD-1128-98
Guide of Good Practices for Occupational Radiological Protection in Plutonium Facilities
-- shielding for extraneous sources of interference such as radiation, radiofrequency,
temperature, and vibration
-- mechanical and electrical ruggedness
-- ease of maintenance and calibration.
A plutonium air sampling program typically includes a system of fixed head air samplers to
quantify air concentrations in the workplace. The basic characteristics of the sampling
equipment remain the same except that there is normally less flexibility in locating the
sampling heads but more flexibility in selecting and operating the counting instrumentation.
In many instances, installed sampling systems may no longer be operational or may be in the
wrong locations. In those instances, portable air sampling systems, both impactor-head type
or filter type may be used to provide required worker protection.
4.1.6 Sample Analysis
Plutonium air samples are typically analyzed by alpha counting, alpha spectral analysis, or
chemical analysis. The technique used will depend upon the filter media used, the physical
and chemical state of the contaminate, the urgency for the data, interfering radionuclides,
and other factors. Authoritative guidance in establishing plutonium air sampling counting
and analysis methods can be found in NCRP Report No. 58, A Handbook of Radioactivity
Measurements Procedures (NCRP, 1985) and in Air Sampling in the Workplace (NRC,
1993).
4.1.7 Monitoring Strategies and Protocols
The rapid, early detection of airborne releases requires knowledge of the potential sources
and characteristics of the airborne material, the locations of the personnel who are at risk,
and the capabilities of the detection devices. Optimally, the samples should be taken
between the source and the potentially exposed worker (or member of the public) to
intercept the airborne materials before they reach the individual. With the numerous sources
and mobility of the workers, interception under all conditions is difficult, if not impossible,
to achieve. Samples of airborne materials should be taken as close to their points of origin
as practicable to maximize the probability of their detection (airborne concentrations are at a
maximum at their points of origin).
Fixed probes that are positioned to intercept releases from recognized major potential
sources should be used along with portable air samplers for planned activities with known
potentials for airborne release of contaminants and for temporary storage of contaminated
materials in areas of low air flow. If the workplace exhaust system can be shown to provide
4-5


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