Isao Yoshikawa

Relationship between the 137Cs whole-body counting results and soil and food contamination in farms near Chernobyl

We measured the radioactivity in the soil and child food samples from farms near Mogilev (56-270 GBq km(-2) 137Cs), Gomel (36-810 GBq km(-2) 137Cs), and Klincy (59-270 GBq km(-2) 137Cs), who had whole-body 137Cs counting results measured as part of a health examination in the Chernobyl Sasakawa Health and Medical Cooperation Project. Soil contamination on the family farm seems to be the main source of human contamination because most of the people in the area live on small farms and they and their domestic animals eat crops from the farms. A clear correlation was found between the childrens whole-body 137Cs counting results and the radioactivity in their food (correlation coefficient: 0.76; confidence level of correlation: 3.2 x 10(-9)). There were also significant correlations between the whole-body 137Cs counting results and both the radioactivity of the soil samples (correlation coefficient: 0.22; confidence level of correlation: 0.0107) and the average contamination level of their current residence (correlation coefficient: 0.20; confidence level of correlation: 0.0174).

Measuring The External Exposure Dose In The Contaminated Area Near The Chernobyl Nuclear Power Station Using The Thermoluminescence Of Quartz In Bricks

We collected bricks from buildings in the heavily contaminated evacuated area of Belarus in a 30-km zone around the Chernobyl nuclear power station and the Gomel-Bryansk area of 150–250 km from Chernobyl and estimated the cumulative radiation dose caused by the reactor accident by measuring the thermoluminescence (TL) of the bricks. The annual dose at each location was measured using glass dosimeters and thermoluminescence dosimeters (TLD). The dose rate was measured using an energy-compensated NaI scintillation survey meter. The soil contamination near the location of each brick was measured using a germanium semiconductor detector. The main purpose of the project was to extrapolate the relation between the cumulative external dose and the present dose rate or contamination level to the lower contaminated areas. The results of the glass dosimeter, TLD, and survey meter determinations were almost identical. For a determination of the annual dose higher than 10 mGy y−1, the cumulative dose by TL (TL dose) was roughly proportional to the annual dose and about 1.5 times larger than the cumulative dose calculated from the annual dose and 137Cs half life. The difference is expected due to the contribution of short-lived nuclides immediately after the accident or localized heavy contamination of the ground surface with 137Cs that migrated afterwards. For annual dose smaller than 10 mGy y−1, the proportionality was not observed and most of the locations facing indoors showed TL doses very much larger than that expected from the proportionality. The cumulative dose outdoors by TL was also roughly proportional to the regional 137Cs contamination level and the proportional constant is about 10−1 mGy per GBq km−2, and is about 250 times larger than the present annual internal dose derived from published results. The correlation between the present dose rate where the brick was sampled and the average 137Cs concentration in the ground soil near the point is not clear, possibly because of the large spatial fluctuation in the 137Cs concentration in the soil.

Distinct difference in relative biological effectiveness of 252Cf neutrons for the induction of mitotic crossing over and intragenic reversion of the white-ivory allele in Drosophila melanogaster.

The relative biological effectiveness (RBE) of 252Cf neutrons was determined for two different types of somatic mutations, i.e., loss heterozygosity for wing-hair mutations and reversion of the mutant white-ivory eye-color, in Drosophila melanogaster. Loss of heterozygosity for wing-hair mutations results predominantly from mitotic crossing over induced in wing anlage cells of larvae, while the reverse mutation of eye color is due to an intragenic structural change in the white locus on the X-chromosome. For a quantitative comparison of RBE values for these events, we have constructed a combined mutation assay system so that induced mutant wing-hair clones as well as revertant eye-color clones can be detected simultaneously in the same individuals. Larvae were irradiated at the age of 80 +/- 4 h post-oviposition with 252Cf neutrons or 137Cs gamma-rays, and male adult flies were examined under the microscope for the presence of the two types of clonal mosaic spots appearing. The induction of wing-hair spots per dose unit was much greater for 252Cf neutrons than for 137Cs gamma-rays, whereas the frequencies of eye-color reversion were similar for neutrons and gamma-rays. The estimated RBE values of neutrons were 8.5 and 1.2 for the induction of mutant wing-hair spots and revertant eye-color spots, respectively. These results indicate that the RBE of neutrons is much greater for mitotic crossing over in comparison to the intragenic white-ivory reversion events. Possible causes for the difference in RBE are discussed.

Changes with age in swimming performance of X-irradiated mice

Abstract The time required to swim 250 cm was determined once weekly for the entire life of fifteen pairs of male dd/K mice. The irradiated group was exposed to a single 224 rad of X-rays at 20 weeks of age. Median survival time (ST50) for the control was 88.9 weeks and that for the irradiated group was 77.4 weeks, and both regression lines relating to death rate and age were parallel. The swimming ability of control mice began to decrease when the mice were 40 weeks of age, after which there was a gradual reduction with age, at 0.00646/day. In the irradiated group, the swimming ability decreased from seven weeks after the irradiation. The time of 50% reduction of swimming speed (TRS50) for the control was 78.9 weeks and that for the irradiated group was 66.3 weeks, and the slopes of the regression lines relating reduction rate and age were similar. Differences between ST50 and TRS50 were 10 weeks in the control and 11 weeks in the irradiated group, respectively. These results indicate that there is no basic difference in the reduction in swimming ability between control and irradiated mice. The X-irradiation may simply mean that the reduction in the swimming ability is displaced to an earlier time, with no alteration in the rate of reduction, and that the earlier appearance in the irradiated group is related to premature aging as induced by irradiation.