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24the teeth <strong>of</strong> 6,000 children and found that childrenborn soon after the Chernobyl catastrophehad 10 times more Sr-90 in their teethcompared with children born in 1983 (Ecologist,2000).Problem <strong>of</strong> Americium-241. The powerful alpharadiation emitter Am-241, formed as a result<strong>of</strong> the natural disintegration <strong>of</strong> Pu-241, isa very important factor in the increasing levels<strong>of</strong> contamination in many areas locatedup to 1,000 km from the Chernobyl NPP.The territory contaminated by Pu today, wherethe level <strong>of</strong> alpha radiation is usually low, willagain become dangerous as a result <strong>of</strong> the futuredisintegration <strong>of</strong> Pu-241 to Am-241 inthe ensuing tens and even hundreds <strong>of</strong> years(see also Chapter III.9). An additional danger<strong>of</strong> Am-241 is its higher solubility and consequentmobility into ecosystems compared withPu.1.6. Lead ContaminationDuring operations to quench the fires inthe fourth reactor <strong>of</strong> the Chernobyl NPP, helicoptersdumped 2,400 tons <strong>of</strong> Pb into the reactor(Samushia et al., 2007; UNSCEAR, 2000);according to other data, the figure was 6,720tons (Nesterenko, 1997). During several subsequentdays, a significant part <strong>of</strong> the Pb wasspewed out into the atmosphere as a result <strong>of</strong> itsfusion, boiling, and sublimation in the burningreactor. Moreover, Pb poisoning is dangerousin itself, causing, for example, retardation inchildren (Ziegel and Ziegel, 1993; and manyothers).1. Blood Pb levels in both children and adultsin Belarus have noticeably increased overthe last years (Rolevich et al., 1996). In theBrest Province <strong>of</strong> Belarus, for example, <strong>of</strong>213 children studied, the level <strong>of</strong> Pb was0.109 ± 0.007 mg/liter, and about half<strong>of</strong> these children had levels <strong>of</strong> 0.188 ±0.003 mg/liter (Petrova et al., 1996),whereas the World Health Organization(WHO) norm for children is no more than0.001 mg/liter.2. In Ukraine in the Poles’e District <strong>of</strong> KievProvince,levels<strong>of</strong>Pbintheairbreathedby operators <strong>of</strong> agricultural machinerywas up to 10 times or more, exceedingmaximum permissible concentrations. Increasedlevels <strong>of</strong> Pb were apparent in thesoil and atmosphere and in the urine andthe hair <strong>of</strong> adults and children in Kievsoon after the explosion (Bar’yakhtar,1995).3. Pb contamination added to radiationcauses harm to living organisms (Petinand Synsynys, 1998). Ionizing radiationcauses biochemical oxidation <strong>of</strong> free radicalsin cells. Under the influence <strong>of</strong>heavy metals (such as Pb) these reactionsproceed especially intensively. Belarussianchildren contaminated with both Cs-137and Pb have an increased frequency <strong>of</strong>atrophic gastritis (Gres and Polyakova,1997).1.7. Evaluation <strong>of</strong> Chernobyl’sPopulation DosesThe International Atomic Energy Agency(IAEA) and WHO (Chernobyl Forum, 2005)estimated a collective dose for Belarus, Ukraine,and European Russia as 55,000 persons/Sv. Byother more grounded estimates (see Fairlie andSumner, 2006) this collective dose is 216,000–326,000 persons/Sv (or even 514,000 persons/Svonly for Belarus; National BelarussianReport, 2006). The worldwide collective dosefrom the Chernobyl catastrophe is estimatedat 600,000–930,000 persons/Sv (Table 1.6).However, it is now clear that these figuresfor collective doses are considerably underestimated.1.8. How Many People Were andWill Be Exposed to Chernobyl’sContamination?The first <strong>of</strong>ficial forecasts regarding thehealth impact <strong>of</strong> the Chernobyl catastrophe

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