EFFECTIVE ARRIVAL TIME (HOURS) O 6 , 7 | GROUND 8 ] 9 { IO 1 | oI l2 ff 13 1 14 I 15 | 16 1718 1920 | 300 3000_ RONGE LAP. (BeAL23P 900 <= 18007900 atoe art — 40 60 od UTIRIK IK }0a-188 —!75 220 RO i 1, AILINGNAE ATOLL |, a 0 1020 7 ATOLL 000 3300 $100. fF BIKAR Pe: 100 ZERO r 80 100 1I20 140 !60 TAKA a me 14 ATOLLW !® es Lt 4 180 200 220 240 260 280 300 320 340 DISTANCE FROM GROUND ZERO (MILES) Figure 1. Approximate gamma dose rates (roentgens per hour) at 3 feet above the ground, one day after the detonation. From Glasstone (40). 2. Residual Radiation To assess potential effects of low-level residual radiation persisting on Rongelap, Utirik, and Bikini, periodic monitoring of the inhabitants of these atolls as well as samples of native flora, were performed. E. fauna, soil, and marine life These studies are discussed in Section X and Appendix II. Data Evaluation Reevaluations of dose estimates are planned or under way using more sophisticated technology and computer methods currently available, and it is possible dose estimates may be increased. In the meantime the dose calculations previously developed will continue to be used. While quantitative variations in dose estimates have an obvious impact on dose/effect correlations, other considerations are equally important in these studies, especially regarding radiation induction of thyroid neoplasms (caveats regarding thyroid dose estimates are discussed in Section IX and Appendix II). Risk probabilities for development of neoplasms secondary to radiation have classically been derived for malignant tumors of specific organ systems.