wf. a paaheubed mba, $eeaten: ++ 1 b 4 t * CATTLE (853 samples) 1.0 o HUMAN (1!65 samples) E —4 2 20.1 > a 2 = 0.01 ° 2 a 3 0.001 ° s LE = 0.000! E ee TESTS” * BRITISH currence of occasional high values re- | quires further study to determine how muchreliance can be placed on the ideas of uniform distribution or uniform accessibility’ of fallout materials. Similar interpretation of occasional high values could not be made for the human samples because any such value was automatically suspect on accountof the widespread medical uses of iodine-131; in compilation, such values were eliminated from averages after the institution of origin confirmed that the individual had been treated with iodine-131. Milk 4 RUSSIAN me U.S.(PACIFIC) 1 U.S. (CONTINENTAL) WH u bbe $ JFMAMJJASONOJFMAMJ JASOND 1955 i956 Fig. 1. Summaryof iodine-13! levels in human andcattle thyroids as correlated with nuclear weaponstests during 1955-1956. nation for cattle; indirect evidence (3) implicating food as the principal source of iodine-131 in cattle provides support for the findings presented in this paper. A comparison of cattle values shown in Table 2 and the average humanlevel is of interest. If the concentration in the thyroids of the barn-fed animals is corrected by’a factor of 5 to accountfor the difference in respiratory tidal volume between the two species, a value of 0.0024 millimicrocurie per gram is obtained. As noted from Fig. 1, this is in fair agreement with the human values for this period (late June 1955). Since it is reasonable to assume that the iodine-131 burden in the barn-fed animals resulted primarily from inhalation, this supports the idea that the human burden may in large measure result from inhalation. Table 1 presents the data for May 1955, a peak month. For ease of interpretation, the results have been lumped by geographical regions. Despite the fact that generalizations about regional differences are not particularly meaningful in Table 3, which presents the percentile distribution of samples for May 1955 and August 1956, two peak months. For instance, during the May peak, 30 percent of the human samples hadless than 0.0008 millimicrocurie per gram, whereas 11 percent had more than 0.01 millimicrocurie per gram; the spread was even greater for the cattle samples. As a further example, out of ten cattle sam- are apparent. As expected, the levels from the region near the Nevadatest sitc were higher than those from the rest of the country. The human values were essentially the same all over the country except for the Nevada-Urah area. The cattle samples, in contrast, appeared to show more differences between regions, with lowest values from the West Coast and highest from the Southwest. This maybe related to the different routes of assimilation of fallout iodine-131 by man and grazing animals. Cattle samples from abroad ‘were generally low. Particular attention is called to the large spread of values. This is illustrated and Portland; five cattle samples from California and Washington) because of arbitrary factors, some trends ples during the period 1 to 15 October 1956, eight ranged between 0.004 and 0.09, whereas the other two samples were 1.6 and 2.0 millimicrocuries per gram. There are obvious reasons for variations within sample groups; however, the oc- It seemed important to consider milk as a route by means of which fallout radioiodine could be transmitted to the human population, especially to children, since appreciable amounts (up to .6 percent) of radioiodine ingested by the dairy cow appears in the milk (7). Sam- ples of milk (100 milliliters) from the same areas as the sources of the cattle thyroids were collected from February to June 1955. No activity was detectable in these milk samples, indicating that the concentration of iodine-131 must have been less than about 0.01 millimi-. crocurie per 100 milliliters when the milk was secreted. From some unpublished experiments by F, W. Lengemann, it was shown that in two dairy cows receiving iodine-131 every day there was, at steady state, 0.74 and 1.3 percent of the daily dose per kilogram of milk and 30 and 65 percent of the daily dose in the thyroid gland, respectively. It is estimated from these values that the levels of iodine-131 in milk from dairy cows ———- Table 1. Iodine-131 content of human andcattle thyroid glands during May 1955. _, Human Location (mpc/g) Nevada-Utah (eight human samples from Salt Lake City; two cattle samples from Nevada and southern Utah) 0.030 West (27 human samples from Los Angeles - Louisville, Oak Ridge, and New Orleans; nine cattle samples from Louisiana, Tennessee, Texas, and Florida) North and Northeast (37 human samples from Minneapolis, Chicago, Boston, and New York: ‘six cattle samples from South Dakota, Missouri, anid Massachusetts) Abroad Panama(two cattle samples) Hawaii (two cattle samples ) Germany (two cattle samples) Greece (one cattle sample) French Morocco (one cattle sample) Tokyo, Japan (one cattle sample) : \ aN 0.0048 South and Southeast (39 human samples from Cattle (mpc/g) Lo > 4630.15 0,086 0.0055 0.46 0.0032 0.18 0.10; 0.082 0.11; 0.081 0.0019; 0.0056 0.013 0.047 0.0092

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