ty -3- Nelson. At Rongelap and Utirik samples were yathered to attempt to correlate radiation levels in soil with adjacent fruit trees (pandanus, coconut, breadfruit) and arrowroot, messerschmidia, scaveola plants for a possible extrapola- tion purposes at Bikini and Eniwetak where vegetation samples are limited. Other samples collected included 24-hour urine samples, water, coconut crabs and certain marine specimens. It will be some time before radiochemical analyses of these samples is completed and the data analyzed. Gamma spectrographic analysis (whole-body counts) were carried out on 22 people at Utirik, 46 at Rongelap and 31 people at Bikini, including members of the families who had returned. These data are undergoing computer analysis. Preliminary analysis of these data give the following estimated average body burdens of 137cs: \ MALES Bikini Utirik Rongelap U.S.Medical Team * No. 18 9 22 6 MCL Body burden 0.129 0.262 0.475 0.0021 FEMALES % MPC 4.3 ‘ 8.7 15.8 0.07 ‘ | HCi No. 13 Body burden 0.073 TMP C 2.6 24 0.317 10.6 13 0.133 + 4.4 Using 3 »Ci MPC-based on the standard 1/10 of the maximum permissible burden for industrial populations which is 30 KCi according to the Recommendations of the International Conmission on Radiological Protection, ICRP Public.2 (1959). A gamma survey was carried out on Bikini Island using a scintillation type - survey meter calibrated for l37Cs which respresents about 95% of the gamma radiation on the island. the island; A. Preliminary analyses showed roughly the following levels on Village (Living area) Inside cement houses with coral covered yards 2.38 Outside cement houses with coral covered yards 3.95 Inside cement houses without yard covered coral 2.98 Outside cement houses without yard covered coral B. Average UR/hr. 9.44 Along village road 13.1 Inaterior-coconut groves 41.6