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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.

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