lneed carcinogenesis than the adult thyroid. 7 Campbell. J. E., G. K. Murphy, A. S. Goldin, H. B. Robinson, C. P. Straub, F. J. Weber and H. Lewis, Am. J. Public Health, 49, 225 (1959). 8 "Strontium Program-Quarterly Summary Report,'' Health and Safety Laboratory Document [SL-55, U.S. Atomic Energy Commission, New York Operations Office (1959). 9 The evaluation of the constant in this equation is based on physical and biological data for ine-131, which have been summarized, for example, in "Recommendations of the International mmission on Radiological Protection," Brit. J. Radiol., Supplement No. 6 (1952). It is assumed It the effective half-life of iodine-131 is 7.7 days and that the effective beta energy is 0.19 Mev. 0 A recent survey of 312 children under the age of six in suburban Long Island by H. H. Neumann, -h. Pediat., 74, 456( 1957), gave a mean value of 840 ml of fluid cow's milk consumed per day h the lower third of the group averaging 647 cc per day and the upper third averaging 1,005 cc day. 1 Since evaporated milk will tend to be several months old before it is consumed, its iodine-131 ivity should be virtually nil. 2 Boyd, E., in Handbook of Biological Data, ed. by W. S. Specter (Philadelphia: W. B. Saunders ., 1956). a Dunning, G. M., Nucleonics, 14, No. 2, 38 (1956). 4 See, for example, R. L. Gunther and H. B. Jones, U.S. Atomic Energy Commission Document 'RL-2689 and addendum (1954). 5 Oddie, T. H., Brit. J. Radiol., 24, 333 (1951). 6 Middlesworth, L. Van, Nucleonics, 12, No. 9, 56 (1954) and Science, 123, 982 (1956); Comar, L., B. F. Trum, U. S. G. Kuhn III, R. H. Wasserman, M. M. Nold, and J. C. Schooley, Science, , 16 (1957). 7 Spiers, F. W., Brit. J. Radiol., 29, 409 (1956). s It should be noted that with the cessation of nuclear weapons testing in November, 1958, nan thyroid levels of radioiodine should decline exponentially and by January, 1959, there ,uld no longer have been any appreciable contamination of milk with radioiodine from past ipons tests. The level of radioiodine in cow's milk may well be the most important index of rt-term environmental contamination with fission products whether from weapons tests or er sources [see discussion in Safety Aspects of Nuclear Reactors, ed. C. R. McCullough (New rk: D. Van Nostrand Co., 1957), 28].