Tatie 22 Soli-mature 12a concentration lfacrors calcuiatea from associated” and 'nonassociated” iata. Tencentration factor. “oCi, = arv diant) Associated Nucilide species Sr, [oaevora Nonassociated Mo. or No. or samples samples fin “sCi/z dry soil) Max Median Min Max Median - 2 ” 5.24 0.41 0.33 4 9.048 4.3 , 1.8 coconut 7 9.099 0.38 0.16 15 0.041 0.74 0.29 “os, Scaevola 2 2.3 14 7.5 4 0.073. “leg, coconut S82 16 3.0 “390, coconut =} SiO -40pn, coconut 4 )~—Ssi«O1—S—«i2L—Ssi.015—ia12~Ss*é‘i ZL 29. a ” 705, V4 a “ ar a ‘ 250.53 7.7 1g 2.6 ~=—S—i«<‘2z«COZD_—sd.0158-s22—S—«<0086——‘<‘ KSC . : 39 . =SsiS S08 : Plant and soil data sampled from the same site. Sprant and soil data sampled from different sites in the same general area. soncentrations expected in the terres- age Eneu-Bikini soil concentrations. trial food products. Since most of the animal diet consists The results are of vegeration and a certain amount of listed in Table 23. soil, this rarioing procedure should During the June survey, a fully zrown pig and two chickens that were sredict reasonable concentrations for born in and raised on Bikini Island domestic animals raised on Eneu. were obtained for analysis. The pig Although coconut crabs were not and chickens roamed freely around the collected during the June 1975 survey, island, so the radionuclide concentra- they were collected during previous tions in these animals reflect their visits to the islands. integrated diet. listed for coconut crab in Table 23 Ingestion via the were determined from data from collec- meat pathway can be estimated by the analysis of these samples. The values The esti- tions in 1969, 1972, and 1974, 9*3t+32 Concentrations in food products after mates of the radionuclide concentra- tion expected in meat on Eneu were June 1975 are calculated assuming that determined by multiplving the concen- the only loss of radionuclides from trations in the meat samples from the environment is the result of the 3ikini Island by the ratio of the aver- Dhysical decay of each radionuclide. -31—