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Health Risks of Ionizing Radiation: - Clark University

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48 Atomic Bomb Survivors<br />

approximating a supralinear curve. For example,<br />

over the dose range 5-20 mSv the ERR estimate is<br />

2.6/Sv and it declines steadily as dose increases 4 .<br />

Solid cancer mortality depends on age at exposure<br />

and gender; specifically, risks are higher for females<br />

and for childhood exposure. The 2003 analysis<br />

generated an average ERR estimate <strong>of</strong> 0.47/Sv<br />

(averaged for both sexes and assuming exposure at<br />

age 30). As in the 1996 analysis, the dose-response<br />

curve was steeper at lower doses so that the ERR<br />

estimate was 0.74/Sv (0.1-1.5) for doses less than<br />

120 mSv. The effect <strong>of</strong> age at exposure was described<br />

as a decrease in the ERR estimate by 36% per 10-yr<br />

increase in age at exposure. Exposures in infancy,<br />

for example, would be associated with a solid<br />

cancer mortality ERR <strong>of</strong> ~1.9/Sv 5 . Delongchamp<br />

et al. (1997) calculated a similar ERR estimate <strong>of</strong><br />

1.4/Sv (90% CI 0.4-3.1) for adult cancer mortality<br />

after exposures in early childhood (less than 6 years<br />

old).<br />

The dose-response pattern <strong>of</strong> leukemia mortality<br />

is best described with a nonlinear model so that<br />

one estimate <strong>of</strong> ERR/Sv would be misleading.<br />

Pierce et al. (1996) presented summary estimates<br />

<strong>of</strong> leukemia mortality risk with an ERR <strong>of</strong> 4.6/Sv<br />

(90% CI 3.3-6.4), apparently based on a linear<br />

model. The effect <strong>of</strong> age at exposure on leukemia<br />

mortality was complicated. Exposures in childhood<br />

were associated with higher risks in the first 10 or 20<br />

years after exposure. If we consider the risk over the<br />

entire follow-up period to date, however, then risks<br />

are about the same for all ages at exposure. This<br />

pattern can also be described by saying that leukemia<br />

mortality risks declined over time, and this decline<br />

was steeper for people exposed in childhood.<br />

4.3 Noncancer mortality<br />

Noncancer mortality through 1990 was assessed<br />

by Shimizu et al. (1999) and additional followup<br />

through 1997 was discussed by Preston et al.<br />

(2003). The pattern <strong>of</strong> deaths from noncancer<br />

diseases showed a strong healthy survivor effect.<br />

This was evident in a lower noncancer mortality<br />

rate among proximal survivors for a few years after<br />

the bombings; the people that were strong enough<br />

to survive the bombings were apparently healthier<br />

than average. This effect diminished over time; to<br />

account for this effect noncancer mortality risks<br />

were estimated based on data from 1968-1997<br />

(Preston et al. 2003). Generally the noncancer<br />

mortality rates were associated with dose, although<br />

the effect was smaller than that seen for cancer, and<br />

the dose-response pattern could be described as<br />

linear. Deaths from stroke, heart disease, respiratory<br />

disease, and digestive disease increased by 10-20%<br />

per Sv (ERR 0.1-0.2/Sv). Blood diseases were an<br />

exception, showing a stronger effect with an ERR<br />

<strong>of</strong> 1.9/Sv (1.2-2.9; Shimizu et al. 1999). There was<br />

some evidence, not significant, <strong>of</strong> an effect <strong>of</strong> age at<br />

exposure that was similar to that seen with cancer<br />

mortality.<br />

4.4.1 Solid cancer incidence<br />

Thompson et al. (1994) analyzed the incidence <strong>of</strong><br />

solid tumors over the period 1958-1987. Generally,<br />

there was a linear dose-response relationship for<br />

cancer incidence with an ERR <strong>of</strong> 0.63/Sv (0.52-<br />

0.74). There was a two-fold greater ERR for females<br />

(0.84/Sv) than for males (0.38/Sv), and a strong<br />

effect <strong>of</strong> age at exposure (Figure 4-5) 6 .<br />

Figure 4-5. ERR estimates for total solid cancer incidence<br />

by gender and age at exposure (based on data from<br />

Thompson et al. 1994).<br />

4 At doses <strong>of</strong> 20-50, 50-100, 100-200, and 200-500 mSv the ERR estimates are 1.6, 0.60, 0.43, and 0.38/Sv,<br />

respectively.<br />

5 Based on the following model: ERR = 0.50d{exp[-0.045(agex-30)]} (Preston et al. 2003).<br />

6 The ERR estimates were 1.90, 1.21, 0.58, and 0.37/Sv for ages 0-9, 10-19, 20-39 and 40+ at exposure.

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