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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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.