Health Risks of Ionizing Radiation: - Clark University
Health Risks of Ionizing Radiation: - Clark University
Health Risks of Ionizing Radiation: - Clark University
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7<br />
MAYAK WORKERS<br />
7.1 Introduction<br />
The cohort <strong>of</strong> Mayak workers is distinctly different<br />
from other worker cohorts in that the average<br />
exposures <strong>of</strong> these workers were much higher and<br />
women made up a greater fraction <strong>of</strong> the workforce.<br />
For this reason we have devoted a separate section to<br />
this cohort. Mayak has also made a pr<strong>of</strong>ound impact<br />
on the communities along the Techa River; this is<br />
discussed in Section 12.<br />
Mayak (the Mayak Production Association), in<br />
the southern Urals region <strong>of</strong> Chelyabinsk, was the<br />
first nuclear complex in the Soviet Union. The plant<br />
included a nuclear reactor, a plutonium production<br />
facility, and a radiochemical fuel separation facility.<br />
<strong>Radiation</strong> exposures during the first few years <strong>of</strong><br />
operation were quite high, with average annual<br />
external doses <strong>of</strong> roughly 0.5 Gy. Exposures declined<br />
following a 20-fold reduction in the maximum daily<br />
permissible dose in 1952 (Koshurnikova et al. 1999),<br />
but were still relatively high- the mean lifetime<br />
dose received by Mayak workers averaged 0.8 Gy,<br />
roughly an order <strong>of</strong> magnitude higher than mean<br />
lifetime doses in most worker cohorts (see Section<br />
6). In addition to external radiation these workers<br />
were exposed to plutonium. Inhaled plutonium<br />
is deposited most heavily in the lungs, and <strong>of</strong> the<br />
plutonium that migrates to the rest <strong>of</strong> the body about<br />
50% is deposited in the skeleton (Koshurnikova et<br />
al. 2000). Deposited plutonium remains in the body<br />
for a long time resulting in chronic exposure to alpha<br />
particles; the mean alpha lung dose in this cohort<br />
was 0.2 Gy. Exposure pr<strong>of</strong>iles varied by facility as<br />
shown in Table 1.<br />
7.2 <strong>Health</strong> effects<br />
Two approaches to this cohort have been pursued<br />
by different teams <strong>of</strong> scientists from Chelyabinsk<br />
and their colleagues- case-control studies <strong>of</strong> lung<br />
cancer (Tokarskaya et al. 1995, 1997, 2002) and<br />
cohort studies <strong>of</strong> total mortality and various causes<br />
<strong>of</strong> death. These studies have been reviewed by the<br />
United Nations Scientific Committee on the Effects<br />
<strong>of</strong> Atomic <strong>Radiation</strong> (UNSCEAR 1994, 2000), by<br />
the Radiological Assessments Corporation for an<br />
analysis <strong>of</strong> plutonium risks around Rocky Flats<br />
Plant (RAC 2000), and recently by Harrison and<br />
Muirhead for a comparison <strong>of</strong> risks from external<br />
and internal radiation (2003). A comprehensive<br />
cohort study <strong>of</strong> mortality in all 21,557 Mayak<br />
workers was presented in 2003 (Shilnikova et al.).<br />
The most apparent health effects in Mayak workers<br />
have been the cancers associated with plutonium-<br />
lung, liver, and bone cancer and leukemia.<br />
Lung cancer. Tokarskaya et al. (1995) found<br />
that lung cancer was associated with plutonium<br />
exposures, gamma exposures, and smoking. No<br />
dose-response analysis was performed for gamma<br />
exposures but the plutonium dose-response curve<br />
that they generated was nonlinear with a threshold<br />
at 0.8 Gy 1 . In 2002 Tokarskaya et al. used an<br />
1 Issues with this dose-response analysis were raised by Jan Beyea (1998); he noted that case-control studies are<br />
not able to distinguish between non-linear dose-response relationships and differences in exposure distributions<br />
between cases and controls.<br />
97