STRONTIUM-90 IN MILE In making comparisons of radiation sources, it must be taken into account that Sr-90 radiation is localized in the bone andall of the other sources of external radiation can not be compared directly because of différences in penetrating power. However, Libby (74) has pointed out that it is possible to compare yn ineom- rage disdiet need directly Sr-90 and casmie ray radiation at the bone level. The f-particles elimi- 1 lonizing many in- nated by Sr-90 and Y-90 decomposition have a tissue penetration of about 2 mm. and this is localized in the bone wherecell formation is taking place. On the other hand, cosmie rays penetrate the whole body, and the ionization density along the tracks of the ~-mesons, which are the principal cosmie ray components to consider in the lower air, is similar to that of the Sr-90 and Y-90 decomposition. Hence, it is possible to equate cosmic-ray dosage and Sr-90 dosage directly, and express cosmie ray radiation in terms of Sunshine Units. Libby (14) notes that the annual cosmic-ray radiation dosage at Washington, D. C. (or any place at sea level at this latitude) is about 37 mr per year and at Denver, Colorado (5,000 ft.), 60 mr per year. This Is equal to about 23 mr per year difference, or is equivalent to 8 S.U. (1 8.U. is about the same as 3 mr per year). The present level of Sr-90 in the bones of children is between 0.5 and 1.0 8.U. and, if testing were to continue at the same rate indefinitely to equilibrium, the level of Sr-90 in human bone would be in the range of 4-21 8.U. (8, 11,14}. This level compared to 8 8.U. derived from cosmic rays at Denver over Washington, suggests that if the level were strong enough to cause leukemia and bone cancer there should be a correlation of such diseases with altitude. Examination by Libby of Public Health records showed that this is not the case (74). It is apparent that the present levels of Sr-90 in bone are contributing a small amount of radiation compared to other sources. If testing were to continue for the next 50 yr. at the same rate, the contribution from Sr-90 in bones would be about equivalent to moving from sea level to 5,000 ft. altitude. At present, the maximiim permissible dose of Sr-90 in bone is 100 8.U. for the average population. The present average level in children is less than 1% of this and will rise only to 4-20% of this, at the extreme, if testing continues. One should also not underestimate the abilities of the atomic scientists. Since it 16, 199). id cumuven time . by high radiation nportant »xidation on ribonests and le dosage ‘adiation doses of ood ecellIs of the doses of ause inortening is shortslated to 1), then yentgens s (19g). lon of a ht, —3.6 | States, ife-time mut 10 r uxImum Fa SapIEE cakien oe y HEtI peoo Wa ERE ars le rays, astum23? ibute to iXternal e variaor some is the U-235 of the atomic bomb detonator which produces Sr-90, and not the hydrogen bombitself, the developmentof a ‘‘clean’’ means of starting the hydrogen bomb would lower or eliminate Sr-90 formation. The radiation produced from a hydrogen bomb is chiefly due to tritium, which is an extremely weak 8 particle emitter. Attempts are now being made to develop such a system. Genetic effects of radiation. While this review has been coneerned chiefly with the significance of Sr-90 in milk, it is unwise to neglect the genetic considerations of the fallout problem. This is necessary because there is not a clear division point between the various phases of the fallout problem. As a source of radiation to the gonads, the Sr-90 derived from food and present in bone is of small consequence because of the low level present and the short penetrating power of the 8 particles. However, the fallout of other isotopes produced in the fission reaction has increased the background radiation. Although this increase [13 ]

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