With the assumption of 10 kg DU spread over 1,000 m2, the top 1 mm of soil in this area contains 1 m3 of soil, weighing 1,500 kg. The DU concentration in the dust will
therefore be 6 µg DU per 1 mg dust.
Normal dust concentration in outdoor air is 50 µg/m3 and under very dusty conditions may reach 5 mg/m3, which would result in DU concentrations of 0.3 µg/m3 and 30 µg/m3 of DU respectively. From a toxicological point of view, these levels are lower than, or within, the
range of given hygiene standards for chronic exposure.
A two-hour stay in a dusty area, such as a field being ploughed, with a respiration rate of 1 m3 per hour, would lead to an intake of 60 µg of DU, corresponding to an effective dose of 7µSv. Even a continuous stay night and day for a year, and under the most dusty conditions, would
not lead to a dose of more than a few tens of mSv. Normal dust conditions would result in a dose 100 times less, i.e. of the order of 0.1 mSv per year. The heavy metal risks are, in allcases, insignificant.
The conservatism in the assumptions is that all DU is respirable and of S-type, and that all DU is distributed in the first upper 1 mm of soil. If, for instance, the measurements should indicate that the DU, if any, is distributed to a depth of 10 cm instead of 1 mm, the
consequences (radiation doses) would be 100 times less with the same area of deposition (10 kg over 1,000 m2) – i.e. a few µSv per year, which is insignificant.