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DOE-STD-1128-98
Guide of Good Practices for Occupational Radiological Protection in Plutonium Facilities
per day (Weinstock and Malm, 1956). See Cleveland (1970) Chapter 2, for more
information.
2.5.2.3 Miscellaneous Radiolytic Reactions
A serious limitation to the use of organic ion exchange materials is their radiation
stability. Brookhaven National Laboratory reviewed the literature and
summarized the effect of ionizing radiation on both organic and inorganic ion
exchange materials (Gangwer et al., 1977). Extraction of plutonium (IV) from
3M HNO3 into 30 vol% tributyl phosphate in kerosene at 5C decreased the
extraction coefficient by a factor of two when irradiated to a dose of 3.6 x 107 R
(Tsujino and Ishihara, 1966). The mechanical properties of thin plastic films
such as polyethylene and polyvinyl chloride degrade with exposure to plutonium.
Cellulose vacuum-cleaner bags will disintegrate in less than a month if used for
housekeeping purposes in plutonium-contaminated gloveboxes.
Leachability of plutonium-containing wastes could be affected by the production
of nitric acid for air-equilibrated dilute salt solutions (Rai et al., 1980).
2.5.2.4 Helium Retention and Release
Helium introduced by alpha-bombardment of plutonium and the alloys and
compounds of plutonium can cause lattice expansion. This was first observed for
plutonium oxides, carbides, and nitrides by Rand et al. (1962) and was later
observed for two plutonium carbide phases. Helium is retained in vitrified
compounds. The retention and release behavior of helium in plasma-torch-fused
Pu02 microspheres for SNAP is an important parameter in the design of the heat
source. Approximately 530 cm3 at standard temperature and pressure (STP) per
year-kg are produced by 238Pu02 (Stark, 1970). Microspheres of 80% 238PuO2 and
20% 239PuO2 that were approximately 50 mm in diameter, prepared by the sol-gel
process, released 92.8% of the helium in 8 months at room temperature
(Northrup et al., 1970). Metals at temperatures well below the melting point trap
the insoluble helium gas in tiny bubbles, which are more or less evenly
distributed through the matrix material (Stevens et al., 1988). Helium buildup in
weapon-grade material is approximately 4 standard cm3 per year-kg.
2.6
OCCUPATIONAL HAZARDS
The major industrial hazard in plutonium facilities is the potential for loss of control of a highly
toxic substance, resulting in either the inhalation or ingestion of plutonium or one of its
compounds by personnel, or the exposure to excessive radiation from a criticality accident. The
2-24


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