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Health Risks of Ionizing Radiation: - Clark University

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12 Introduction<br />

available information and presenting the essence <strong>of</strong><br />

each study with a minimum <strong>of</strong> interpretation.<br />

The optimal organization scheme depends on the<br />

intent and interest <strong>of</strong> the reader; some readers may<br />

be interested in a particular disease, others may be<br />

interested in a particular type <strong>of</strong> radiation, and others<br />

may be interested in specific sources <strong>of</strong> radiation. We<br />

have organized the overview primarily by radiation<br />

source. Natural background exposure and medical<br />

exposure are covered in sections 2 and 3, exposure<br />

to fallout from the atomic bombs and from weapons<br />

testing are covered in sections 4 and 5, and sections<br />

6-9 deal with various occupational exposures.<br />

Section 10 addresses the risks <strong>of</strong> exposure prior<br />

to conception <strong>of</strong> a child (also mainly occupational<br />

exposures). Section 11 deals with the accidents at<br />

Chernobyl and Three Mile Island and Section 12<br />

covers studies <strong>of</strong> communities near nuclear power<br />

and nuclear weapons facilities. We have also included<br />

appendices that deal with specific diseases, leukemia<br />

and thyroid cancer, and an appendix that presents an<br />

analysis <strong>of</strong> the risks associated with preconceptional<br />

exposure (following up on section 10). Each section<br />

includes a brief introduction followed by a review <strong>of</strong><br />

the available epidemiological studies for that source<br />

<strong>of</strong> exposure. At the end <strong>of</strong> each section we have<br />

included a table where we list both quantitative and<br />

qualitative information about each study. We have<br />

not attempted any kind <strong>of</strong> comprehensive summary;<br />

the effects <strong>of</strong> radiation vary by dose, by age at<br />

exposure, and so on, and so such a simple answer<br />

to the question at hand would be misleading. Our<br />

concluding section (section 13) is a discussion that<br />

returns the focus to low doses and considers some<br />

possible interpretations <strong>of</strong> the data.<br />

A few notes on the conventions we adopted for<br />

writing this overview:<br />

• Several acronyms appear regularly throughout<br />

the overview. We have supplied a list <strong>of</strong> acronyms<br />

along with the glossary. The most common will<br />

be the risk units described above (RR, ERR,<br />

OR) and the names <strong>of</strong> certain agencies (National<br />

Cancer Institute, NCI, and Department <strong>of</strong><br />

Energy, DOE). Types <strong>of</strong> leukemia are <strong>of</strong>ten<br />

refered to by their common acronyms (Acute<br />

Lymphocytic Leukemia, ALL, Chronic Myeloid<br />

Leukemia, CML, etc.) and we also periodically<br />

adopt a convention for grouping leukemia and<br />

non-Hodgkin’s lymphoma as LNHL.<br />

• The difference between absolute and relative risk<br />

rests on important biological assumptions. If we<br />

assume that radiation increases an underlying<br />

probability <strong>of</strong> cancer then we use the relative<br />

risk. For example, the number <strong>of</strong> stomach<br />

cancer cases that we expect might depend on the<br />

underlying stomach cancer risk. This is different<br />

between the US and Japan because <strong>of</strong> diet and<br />

maybe other factors.<br />

If, on the other hand, we assume that<br />

radiation confers an independent risk, not<br />

affected by the underlying risk, then we use<br />

the absolute risk concept. Under absolute risk<br />

assumptions a certain dose would produce the<br />

same number <strong>of</strong> cancers in any population.<br />

We have kept our emphasis on the relative risk<br />

model, rather than the absolute risk model,<br />

based on a belief that the relative risk model is<br />

more plausible biologically and in order to keep<br />

the presentation <strong>of</strong> results less cluttered.<br />

• The 95% confidence level is by far the most<br />

common degree <strong>of</strong> confidence; we have<br />

simplified the notation by dropping the ‘95%<br />

CI’ when the confidence interval is 95%, writing<br />

out the confidence level only in those cases<br />

where the author uses another percentage. For<br />

example ‘RR 2.13 (2.00-2.26)’ should be read<br />

as ‘a relative risk <strong>of</strong> 2.13 with a 95% confidence<br />

interval <strong>of</strong> 2.00 to 2.26’.<br />

• We have chosen to use units <strong>of</strong> Gy or Sv for dose.<br />

Where the primary source used rad or rem we<br />

have made the appropriate conversion. We have<br />

also frequently used units <strong>of</strong> mGy (thousandth<br />

<strong>of</strong> a Gray) or mSv (thousandth <strong>of</strong> a Sievert).<br />

If you read through the overview in order you might<br />

notice small differences from section to section. This<br />

is because we wrote this as a large and revolving team<br />

and authorship varied by section. We have done our<br />

best to preserve the document’s fluidity and intent<br />

throughout. Any questions, suggestions for updates,<br />

or comments can be addressed to Octavia Taylor at<br />

the George Perkins Marsh Institute.

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