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Health Risks of Ionizing Radiation: - Clark University

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The terminology associated with radiation and<br />

radiation dose is very confusing. There are units <strong>of</strong><br />

radioactivity, <strong>of</strong> energy deposited in matter, and <strong>of</strong><br />

biologically relevant dose. In addition, two common<br />

units (rad and rem) have been replaced with larger<br />

units for the same things (grays and sieverts). The<br />

units are:<br />

• Curie (Ci). The curie is a unit used to<br />

measure radioactivity. One curie is a quantity<br />

<strong>of</strong> a radioactive material that will have<br />

37,000,000,000 transformations, or nuclear<br />

decays, in one second. Often radioactivity is<br />

expressed in smaller units like a thousandth <strong>of</strong> a<br />

curie (mCi), a millionth <strong>of</strong> a curie (uCi) or even<br />

a billionth <strong>of</strong> a curie (nCi).<br />

• Becquerel (Bq). A Becquerel is a unit that<br />

describes one radioactive disintegration per<br />

second and is therefore a much smaller version<br />

<strong>of</strong> the curie. There are 37,000,000,000 Bq in one<br />

Ci.<br />

• Gray (Gy). The gray is a unit <strong>of</strong> absorbed dose.<br />

This relates to the amount <strong>of</strong> energy actually<br />

deposited in some material, and is used for any<br />

type <strong>of</strong> radiation and any material.<br />

• Rad. The rad (radiation absorbed dose) is the<br />

older unit <strong>of</strong> absorbed dose. One rad is equal to<br />

0.01 Gy.<br />

• Sievert (Sv). The sievert is used to express<br />

effective dose, or the biological damage<br />

potential <strong>of</strong> some amount <strong>of</strong> radiation. Effective<br />

dose is typically calculated by multiplying the<br />

absorbed dose by a factor specific to the type <strong>of</strong><br />

radiation. This is usually called a quality factor<br />

or relative biological effectiveness factor. For<br />

low-LET radiations this factor is typically close<br />

to or equal to one so that one Sv is approximately<br />

equal to one Gy. For high-LET radiations like<br />

alpha particles the factor might be as high as<br />

twenty.<br />

• Rem. The rem (roentgen equivalent in man) is<br />

the older unit <strong>of</strong> effective dose. One rem is equal<br />

to 0.01 Sv.<br />

For this overview we have chosen to use units <strong>of</strong> Gy<br />

or Sv for dose. Where the primary source used rad<br />

or rem we have made the appropriate conversion.<br />

1.6 Epidemiological methods<br />

Introduction 7<br />

Epidemiology is the statistical study <strong>of</strong> disease in<br />

human populations. In epidemiological studies<br />

researchers attempt to identify and analyze<br />

relationships between health effects and possible<br />

causes. This is difficult, in general, because there are<br />

many confounding factors in any study that make a<br />

simple cause-and-effect relationship hard to isolate.<br />

In studies <strong>of</strong> cancer these confounding factors might<br />

include, among other things, genetic predisposition<br />

or exposure to carcinogens other than the one<br />

being studied. If a study population demonstrates<br />

an elevated cancer rate these confounding factors<br />

make it hard to determine the cause. There is also<br />

considerable uncertainty in any epidemiological<br />

study. Researchers can never exactly quantify<br />

exposure or the true background rate <strong>of</strong> a disease,<br />

for example. Uncertainties in studies <strong>of</strong> cancer are<br />

compounded by the random nature <strong>of</strong> cancer: Out<br />

<strong>of</strong> a group <strong>of</strong> people exposed to a carcinogen some<br />

might get cancer and some might not; this is partly<br />

determined by chance.<br />

Epidemiological studies <strong>of</strong> low-dose radiation<br />

present several unique challenges. People are exposed<br />

to radiation from a variety <strong>of</strong> sources, both natural<br />

and manmade, and as we discussed above there is<br />

considerable variability in this exposure. Although<br />

we can estimate average exposures we never know<br />

exactly how much radiation an individual has been<br />

exposed to or from what sources this radiation<br />

came. When we consider that people are always<br />

experiencing some background radiation exposure<br />

(and exposure to other carcinogens), and that there<br />

is always a background cancer rate, the effects <strong>of</strong><br />

small additional doses can be very hard to detect.<br />

In some cases, such as workers at nuclear weapons<br />

facilities, researchers have some idea <strong>of</strong> individual<br />

exposures from measurements that have been made.<br />

In other cases, for example communities around<br />

nuclear facilities, there are no such measurements.<br />

Statistical significance. Because <strong>of</strong> these<br />

difficulties epidemiological studies cannot prove<br />

or disprove causation. Instead epidemiological<br />

studies can suggest associations; these associations<br />

carry statistical power based on how strong the<br />

relationship is and how well the study was designed.

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