RADIOLOGICAL CLEANUP OF ENEWETAK ATOLL 90 rf 4 \ 2 i 1 o£. abtgy’ A socal 4. com a eo ete een { ' A aiken \ Souttwertt Punage N 7 nem a“ a Ara ii eRaoe ores PS) . *y eo os LZ “ re X \ . RADIOLOGICAL PROBLEMS AND ISSUES: 1974 1 2 3 4 ANANW Cp 7th Sb jem het Deep Entrance | | rl x Es nonaNDAEIOK @ Te Wida Parepe ; i ENEWETAK ‘E Ty o7�� we Case Summary: 1. Jee intarisiend Trovel Pu CleanupYoLessThan To Less Than49 40pCr’g On Soken, Lujor & Runit PuCleanup 2. No Restrictions On Fishing. + Pomc ttanc 3. All Radioactive Scrap To Be Cleaned Up From All Islands. “e~ Uniimited Ute of Hid Birds & Epgt 4. Physical Hazard & Obstructive Debres Cleanup On All Islands. oF Coconut Crab island &. Liveon Southern Ilands, Jinedrol Through Kidrenen Unlimited Fishing t sevene TP Subsistence Agriculture Except for Pandanus & Breadfruit omarAt ia Except That Pandanus & ™ Te Untimited Agricutture ® How much radioactivity is there? How much radioactivity is too much? How can one remove any excess radioactivity? How can one dispose of any excess radioactivity? The data on locations and amounts of radioactivity provided by the Enewetak Radiological Survey were adequate for development of general plans and gross cost estimates for removal of all or part of it. However, as 5&5 LEGEND The cleanup and disposal of radiological hazards at Enewetak Atoll posed problems which still have worldwide interest. Cleanup of radioactive contamination and disposal of radioactive waste are potential peacetime problems for the nuclear nations, as well as attendant problems during nuclear war. Enewetak Atoll was not the first peacetime radiological cleanup project. It was preceded by more limited efforts at Palomares, Spain; Thule, Greenland; Bikini Atoll; and Los Alamos, New Mexico. They all posed the same basic questions: © ® @ MEDREN “f =F® Tr Nautical Miles *S Bre No Restrictions On Travel © Pu-239 Cleanup To Less Than 40pCi/g seher eert> wwe " JEDROL ve Of JAPTAN D Tre Lagoon - Rt 77% IKUREN +—~. a NINEDRAL £ TO yvan h “My INEOROL 4 FE Te : . ° or Pt ned eras . et fl BOKEN net 4 Fewer o a ee wr 6G \ SUNIOR404? ~~ ; approving and funding the project; and this, in turn, was contingent on the action agencies resolving the radiological cleanup problems and developing more complete cleanup plans and funding programs. Orcese \ RUNIT &) rd 7 wr o 9] | nt . aen | 1a Planning and Programming the DEIS indicated, detailed field surveys would be required to provide the precise data needed before radiological cleanup could begin. Identifying contaminated debris is relatively simple compared to the problem of detecting and measuring contamination in soil. The Enewetak Radiological Survey and DEIS referred to soil contamination in terms ofactivity level per unit weight of soil Le., measurements of pCi/g. Sampling every gram on every island was clearly impractical, even if it had been possible. The technology for conducting radiological field surveys of contaminated soil was still in the developmental stage and it remained so until well into the actual cleanup operations. This problem did not delay development of the EIS or MILCON program, however. Probably the most complex radiological question was (andstill is): What FIGURE 2-5. ENEWETAK ATOLL, CASE 3. amounts of radioactivity constitute a hazard? Answering that question requires data on the potential sources of exposure (air, water, soil, food, etc.); access to exposure (lifestyle, diet, etc.); organs affected (lungs, elemenchnneprnen hemnhamntaleereeenbereareeeeeteares known before a dose assessment can be made and the hazard can be evaluated. Many of the comments on the DEIS recommended actions to quantify these factors, such as including the contribution from ground water in the dose estimates,!!1.1!2.1!13 conducting an air sampling