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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72 <strong>Radiation</strong> Workers<br />
• 50 rem (0.5 Sv) per year for the shallow dose<br />
equivalent (SDE), which is the external dose to<br />
the skin or to any extremity.<br />
• For workers under 18, the annual occupational<br />
dose limits are 10 percent <strong>of</strong> the dose limits for<br />
adult workers.<br />
• For protection <strong>of</strong> the embryo/fetus <strong>of</strong> a declared<br />
pregnant woman, the dose limit is 0.5 rem (5<br />
mSv) during the entire pregnancy 2 .<br />
In order to remain in compliance with<br />
occupational exposure regulations the owners <strong>of</strong><br />
nuclear facilities must monitor the exposure <strong>of</strong> their<br />
employees. The first external monitoring devices were<br />
pocket ionization chambers and pocket dosimeters;<br />
these were basically pen-sized tubes containing a<br />
wire with an electrical charge that decreased upon<br />
exposure to radiation (Figure 6-2a). These devices<br />
were later replaced by film dosimeters, which were<br />
less expensive, more reliable, and could be attached<br />
to a worker’s security badge. The film on the badges<br />
reacted to radiation by darkening and could later<br />
be analyzed to estimate exposure (Figure 6-2b).<br />
Some facilities switched to thermoluminescent<br />
dosimeters in the early 1970s. These dosimeters<br />
contain light-emitting crystal phosphors that can be<br />
read by a computer after they have been exposed to<br />
radioactive energy. In 1994 researchers found that<br />
Figure 6-2(a). The first external monitoring devices were<br />
pocket ionization chambers and pocket dosimeters<br />
(basically tubes the size <strong>of</strong> pens containing a wire with<br />
an electrical charge that decreased upon exposure to<br />
radiation) (http://www.ieer.org/sdafiles/vol_8/8-4/devices.<br />
html).<br />
2 www.state.ma.us/dph/rcp/faq13.htm<br />
3 tis.eh.doe.gov/ohre/new/findingaids/epidemiologic/ rockyplant/employ/intro.html<br />
many film badges worn from 1953 to 1967 had been<br />
consistently misinterpreted, causing exposures to be<br />
underestimated 3 . In the early stages <strong>of</strong> monitoring<br />
workers for radiation exposure nasal swipes were<br />
used for internal alpha radiation monitoring; this<br />
method was later found to be unreliable. Urine<br />
and blood sampling was added, and when used in<br />
conjunction with the nose swipes, provided better<br />
estimates <strong>of</strong> internal exposure 3 .<br />
Assessing risks. There are many factors to<br />
consider when determining the health risk involved<br />
with occupational exposure. Researchers can compare<br />
disease incidence among workers with national or<br />
local populations, for example using standardized<br />
mortality ratios (SMRs), but this task is complicated<br />
by the fact that workers usually exhibit lower<br />
disease rates and lower death rates than the general<br />
population. This is a predictable situation because<br />
the ill, weak and disabled are usually excluded from<br />
employment; among epidemiologists this pattern is<br />
referred to as the healthy worker effect. This can be<br />
dealt with by comparing disease rates in exposed<br />
workers to disease rates in similar groups <strong>of</strong> workers<br />
who are not exposed to radiation. In section 5, for<br />
example, we saw how military personnel who were<br />
exposed to fallout from nuclear weapons testing<br />
were compared to military personnel who were not<br />
present at the tests. This is <strong>of</strong>ten not done, however.<br />
Figure 6-2(b). Pocket dosimeters were replaced by film<br />
badges. A worker here is pictured checking film badges in<br />
1974 (imglib.lbl.gov/...index/97702936html.