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| DOE-STD-1128-98
Guide of Good Practices for Occupational Radiological Protection in Plutonium Facilities
2.3.3.5 Plutonium Chlorides
Chloride salts, which are a very important category of residues, are byproducts of
pyrochemical operations. Pyrochemical chloride-based operations currently in
use include:
-- DOR
-- electrorefining (ER)
-- molten salt extraction (MSE)
-- pyroredox.
Treatment of chloride-based residues is especially challenging for aqueous
recovery techniques because of corrosion problems with stainless steel
equipment. At the LANL site, Kynar-lined gloveboxes were to be installed to
evaluate their behavior in production-scale operations. The Rocky Flats Plant
(RFP) has also had extensive experience in aqueous recovery of plutonium from
chloride-based residues (Muscatello et al., 1986a, 1986b, 1987). Cesium
chloroplutonate, Cs2PuCl6, was proposed as a primary analytical standard due to
its stability to alpha radiolysis and may now have application as a storage form.
It was first prepared by Anderson (1949). There is no evidence of water
absorption at relative humidities as high as 53% (Miner et al., 1963). After 64
days at 90% relative humidity, Cs2PuCl6 forms a paste.
2.3.3.6 Plutonium Fuels
Plutonium and plutonium-uranium fuel mixtures were developed and tested in
experimental reactors to prove the feasibility of operating power reactors. These
fuels included both liquids and solids consisting of alloys and ceramic mixtures.
Wick (1967) and Schneider and Roepenack (1986) provide comprehensive lists
of fuels. Because of their pyrophoric nature, some of these alloys and
compounds require special care and handling when exposed to reactive liquids or
gases.
2.4
RADIOLOGICAL EFFECTS ON HUMANS
The radiobiological properties of plutonium and other transuranic (TRU) elements are known
primarily from experiments performed on rats, dogs, baboons, and rabbits. Human data on
plutonium are limited. Reviews of the vast literature on plutonium include Hodge et al. (1973);
ICRP 19 (1972); ICRP 30, Part 1 (1979); ICRP 48 (1986); ICRP 30, Part 4 (1988b); and
Liverman et al. (1974). ICRP 30, Part 1 (1979) and ICRP 48 (1986) report different gastro-
intestinal (GI) absorption and biodistribution parameters. The committed effective dose
equivalents, calculated using the models of the two publications, will differ by about 10%, with
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