Secondary Logo

Journal Logo

Radiation-Exposed Populations: Who, Why, and How to Study

Simon, Steven L.; Linet, Martha S.*

doi: 10.1097/HP.0000000000000006

Everyone is exposed to natural and manmade ionizing radiation that can originate from sources in the environment and in medical and occupational settings. There is notable variation, however, among individuals and across populations in the types of sources of radiation and in the frequency, level, and duration of exposure. Adverse health effects associated with radiation exposure have been known for decades, and ionizing radiation exposure has been linked with a broad range of different types of cancer and benign neoplasms as well as birth defects, reproductive effects, and diseases of the circulatory, hematologic, and neurologic systems. Our present understanding of radiation-related health risks derives primarily from multidisciplinary health risk (epidemiologic) studies that provide the key information on radiation-associated health outcomes, quantify radiation-related disease risks, and enhance understanding of mechanisms of radiation-related disease pathogenesis. Such information is central to quantifying risks in relation to benefits; addressing public concerns, including societal and clinical needs in relation to radiation exposure; and providing the database needed for establishing recommendations for radiation protection. Because of the importance of determining risks compared to benefits for all situations where exposure to ionizing radiation might result, it is useful for planning new health risks studies to categorize exposed populations according to the sources and types of radiation. This paper describes a wide range of populations exposed to radiation and the motivation and key methodological criteria that drive the rationale and priority of studying such populations. Also, discussed are alternative methods for evaluating radiation-related health risks in these populations, with a major focus on epidemiologic approaches. This paper concludes with a short summary of major highlights from radiation epidemiologic research and important unanswered questions.Introduction of Exposed Populations (Video 1:29,

*Division of Cancer Epidemiology and Genetics, National CancerInstitute, National Institutes of Health, 6120 Executive Blvd, Bethesda, MD.

The authors declare no conflicts of interest.

For correspondence contact Steven L. Simon, Division of Cancer Epidemiology and Genetics, National Cancer Institute, National Institutes of Health, 9609 Medical Center Dr., Bethesda, MD 20892-9778 or email at

Supplemental Digital Content is available in the HTML and PDF versions of this article on the journal’s Web site (

(Manuscript accepted 16 August 2013)

Back to Top | Article Outline


EVERYONE IS exposed to natural and manmade ionizing radiation that can originate from sources in the environment and in medical and occupational settings. The use of radiation in evolving technologies for diagnosis and treatment of many diseases has revolutionized medical care, but it also exacts a cost in subsequent radiation-related secondary disease risks. Occupational radiation exposures of medical and nuclear power plant workers (as well as astronauts, industrial radiographers, and those working in the aviation and other industries) must be considered when determining radiation protection measures, given the significant societal benefits provided by these workers. Natural background radiation (terrestrial gamma rays, cosmic rays, radon) is ubiquitous and exposes everyone regardless of country of residence. On a much smaller scale, there are a few populations that have been exposed to undesirable events involving radiation in the context of warfare and industrial accidents. Intermediate in numbers are the populations exposed to fallout from nuclear testing. Collectively, radiation exposure affects potentially all people everywhere on earth, and for that reason, it is imperative to understand the associated risks.

There has been limited cataloging of radiation-exposed populations in the literature that enumerates the numbers of persons exposed, typical radiation doses received by members of the population, and for some populations, quantitative measures of disease risks to address public health and radiation protection considerations (e.g., UNSCEAR 2008). Such listings, however, have rarely considered other attributes of radiation-exposed populations and how those attributes may be used to set priorities for conducting studies of health risks that can address public health, clinical, and societal concerns about radiation exposure.

While adverse health effects from ionizing radiation have been known for >100 y, it has taken decades of health risk (epidemiologic) and clinical studies to link radiation exposure quantitatively with several types of cancer and other nonmalignant disorders. The process of quantification of radiation-related disease risks has been derived primarily from analytic epidemiologic studies, while epidemiologic, animal, molecular, functional biomarker, and genetic studies have increased understanding of radiation-related pathogenesis.

This paper describes a broad range of radiation-exposed populations and discusses their key population and radiation exposure attributes. The rationale for studying radiation-related health risks is described, and alternative approaches for evaluating radiation-related health risks are discussed. This paper identifies important population, exposure, and methodological issues that must be weighed when determining feasibility and priority of studying radiation-exposed populations. The paper concludes with a brief list of important unanswered questions.

Back to Top | Article Outline


Who are the radiation-exposed populations?


To identify “radiation-exposed populations,” key terms of reference must be defined. “Exposure” within the radiation sciences has a long history because the term has been used as a quantifiable index of ionization in air (ICRU 1980). More generally, radiation exposure means being subjected to an ionizing radiation hazard, either by irradiation or contamination. In the context of radiation safety and protection, “exposed population” means any identifiable group of persons that has received a radiation dose. The dose is generally associated with emissions from a specific, identifiable radiation source. While it is reasonably simple to identify populations likely to have been exposed (e.g., persons living in the vicinity of a nuclear power plant accident), it is more difficult to determine whether specific individuals were exposed or not. This difficulty is related, in part, to the ambiguity of determining, specifying, or measuring “exposure.”

To ascertain whether a specific person was exposed to radiation, evidence of exposure can be derived from several types of measurements, including a dosimeter that a person might have worn, radiant emissions from a person’s body reflecting internal or surface contamination, or observations of specific biological changes consistent with exposure to ionizing radiation (e.g., changes in chromosomes, tooth enamel, or other tissues) (ICRU 2002). Determining exposure on an individual level is further complicated because all types of measurements have minimum limits of detection that prohibit ascertainment of exposures lower than the minimum limits of detection of the device. Fortunately, however, in the context of learning about health risks, determination of “who is exposed” is less important than identifying a target population in which all members may have been exposed. Within the target population, individuals may have received doses at levels that are quite similar or highly variable, ranging from very low (e.g., nearly indistinguishable from zero) to very high, depending on the exposure conditions. Identification of populations exposed to radiation is but the first step in determining which populations may be useful to consider for epidemiologic studies.

Back to Top | Article Outline

Sources of radiation exposure

Cataloging of radiation-exposed populations requires recognition of sources of exposure and populations that are proximate to the sources or to the emanations from the source in the case of releases of radioactive material to the environment. Exposed populations may include:

  1. persons exposed to natural background sources of radiation (e.g., radon, terrestrial gamma, or cosmic radiation) (Table 1);
  2. patients who have undergone diagnostic image-guided, interventional procedures, radiotherapy, or other medical procedures involving ionizing radiation (Table 2);
  3. persons exposed as a consequence of their occupation (e.g., those employed as medical radiation workers or in the aviation or nuclear energy industries) (Table 3); and
  4. persons exposed to radiation or radioactive releases from wartime events, from nuclear accidents and nuclear testing, or for security reasons including airport security screening (Table 4).
Table 1

Table 1

Table 2

Table 2

Table 3

Table 3

Table 4

Table 4

Identification of radiation-exposed populations generally requires recognition of the source of radiation as well as recognition of a population that was likely to have been in contact with the radiation source or emissions from the source.

Back to Top | Article Outline

Sources of information about radiation exposure

An exposed population, by definition, is composed of individuals who have been or are likely to have been exposed, a condition often assumed based on proximity to the source. While identification of exposed populations is sometimes based on proximity (i.e., not based on evidence of individual exposures) for some populations (e.g., nuclear workers or radiologists), radiation exposure of members of the population may be verified by individual exposure records. Occupational doses can often be verified on an individual level more easily and reliably than in many other exposure situations because of the monitoring and recording requirements imposed by regulation. In contrast, patients exposed to radiation therapy do not have individual exposure measurements, though often doses to individuals can be determined retrospectively from records of the “administered radiation dose” (e.g., for external beam radiotherapy) or from the description of the medical protocol used (e.g., the “administered activity” in the case of nuclear medicine). In turn, the exposure data allows estimation of doses to the treatment field or targeted organ as well as to organs and tissues outside the field or targeted organ. Both estimates may be valuable for health risk studies, depending on the purpose and design of such studies.

In contrast to radiotherapy, exposure records are almost never available from diagnostic radiologic imaging. Medical records do not provide information on dose from diagnostic imaging examinations, nor is such information available from radiology department records. However, data on the number of examinations received by the individual as derived from their medical record and from questionnaires and interviews, as well as hospital imaging protocols, can be useful in deducing a patient’s individual radiation exposure. In all of these examples, which include workers in nuclear facilities and patients undergoing radiotherapy, computed tomography (CT), or other diagnostic imaging procedures, the population of potentially exposed persons can be identified even if individual exposure data are limited.

There are numerous sources of information on radiation exposures in a variety of populations and contexts (e.g., NA/NRC 2006; Simon et al. 2006a and b; UNSCEAR 2008; NCRP 2009; Wakeford 2009).

Back to Top | Article Outline

Uncertainty of exposure of populations

Within an exposed population, there is a true, often unknown, dose received by each person and sometimes a known, but fallible, estimate of dose. How close the estimated dose is to the true dose is often difficult to ascertain without empirical validation measurements, though contemporary uncertainty analysis strategies (e.g., Monte-Carlo modeling) can often bound the possible values of the true dose by a confidence or credibility interval (e.g., NCRP 2009). Recognizing that true doses for individuals cannot be known with certainty, one other uncertain attribute of exposed populations is the range of true doses received. The importance of understanding the range of doses received in the population is related to the need for deriving a meaningful dose-response over a wide range of doses.

Back to Top | Article Outline

Radiation risk: The basis and reasons for study

The findings and quantitative assessment of health risks in humans derive primarily from epidemiologic studies. Many, but not all, of the findings in humans have been confirmed in animal studies (UNSCEAR 1988; NA/NRC 2006; Dupont et al. 2012). Radiobiology studies, in conjunction with epidemiologic and experimental animal investigations, have provided data critical to the understanding of radiation-related disease pathogenesis (UNSCEAR 2006, 2012; Little et al. 2013).

The history of understanding radiation risks has evolved continually, at least from the early part of the 20th century. Within a few years after the initial use of x-rays for radiologic imaging, clinical reports described skin carcinomas, leukemia, dermatitis, cataracts, and other serious conditions associated with radiation exposures of physicians, other health workers, and patients (Frieben 1902; Scott 1911). From decades of research, data from studies of humans have consistently linked moderate to high doses of ionizing radiation exposure with increased risk of many different forms of cancer (Boice 2006), certain benign neoplasms (Neglia et al. 2006), radiation-induced dermatitis (Hymes et al. 2006), cataracts (Ainsbury et al. 2009), and diseases of the circulatory (Little et al. 2012; Darby et al. 2013), hematologic (Ichimaru et al. 1972; Iwanaga et al. 2011), and neurologic systems (Boice 2006; UNSCEAR 1994, 2000, 2006, 2008; NCRP 2013). High radiation doses to pregnant women during weeks 10–27 of gestation may cause severe mental retardation and decrease in the intelligent quotient of offspring (NCRP 2013).

Back to Top | Article Outline

Modification of health effects by individual characteristics, lifestyle, and other factors

Increasingly, epidemiologic and, to a lesser extent, animal studies have demonstrated differences in radiation-related disease risks according to age at initial exposure, gender, ethnicity, and genetic factors within and across populations (Allan 2008). Patients with certain hereditary cancer syndromes can experience increased cancer risks when undergoing radiotherapy (Kleinerman 2009). Accumulating data, however, point to other potential modifiers of radiation-related disease risks, including cigarette smoking, reproductive factors, specific chemotherapy drugs, and possibly other factors (Travis et al. 2003; Cardis et al. 2005; Karagas et al. 2007; Furukawa et al. 2010; Egawa et al. 2012). Improvements in radiation dose measurement in the past few decades have been notable, but increasing knowledge about the long latency of many radiation-related late health effects motivates the need for high-quality historical dose reconstruction along with identification and incorporation of quantitative measures of uncertainty in dose. With growing recognition of the sensitivity of the fetus, young children, and adolescents to radiation-related carcinogenesis (ICRP 2003; Ronckers et al. 2008; NCRP 2013), the dramatic growth in medical radiation exposures to the general population since 1980 (NCRP 2009), and the lifetime nature of radiation-related risks, increasing emphasis has been placed on estimating future radiation-related disease risks using accurate risk projection statistical models. In estimating risks for sensitive population subgroups. These models can account for potential confounding and measures of uncertainty in dose.

Back to Top | Article Outline

Public health value of radiation epidemiologic studies

From the public health perspective, there are several important reasons why quantification of health risks from radiation exposure is important. First and foremost is society’s responsibility to use radiation for greater benefit than harm. Equally important, however, is the large number of persons exposed each year either for intended or unintended reasons. Because of the widespread use of radiation in medicine and industry, the potential benefit to society is great, but similarly, the potential for harm is substantial. Public health studies, by definition, are designed to prevent disease and promote health. The continuous evolution of medical imaging and other devices involving ionizing radiation necessitates timely reviews of the risks and benefits of each new generation of technology.

In addition to the fundamental purpose of establishing a net benefit for the use of devices that emit ionizing radiation, it is important to determine whether radiation exposure is associated with health outcomes for which the evidence is limited, such as chronic lymphocytic leukemia, prostate cancer, or uterine myomata (Boice 2006). For that purpose in particular, epidemiologic studies with high-quality exposure assessment and adequate statistical power are needed to quantify health risks to estimate the disease burden associated with radiation exposure. Such studies are crucial for quantifying the response (health outcome) per unit dose and for providing insight into disease pathogenesis to clarify whether a statistical association is etiologic.

The presence of a statistically significant dose response in epidemiologic studies is useful, at least in a conceptual framework, for establishing appropriate radiation protection guidelines. The dose response provides the incremental risk for incremental additions in exposure. This information is needed for devising appropriate risk protection measures. To characterize the dose-response relationship, reasonably accurate estimates of past radiation doses are needed, along with quantification of potentially important modifiers of dose, and the information to adjust for possible confounding factors (e.g., socioeconomic status, environmental or behavioral factors linked with both the radiation exposure and the disease outcome under study).

For public health reasons, there is a particularly great value to initiate high-quality radiation epidemiologic studies to ascertain and monitor health risks of patients undergoing radiologic imaging procedures that are carried out in large numbers. Such procedures include, but are not limited to, CT, repeated fluoroscopic procedures for patients with inflammatory bowel disease, children with repeated urinary tract problems, and many others. Moreover, it is important to consider conducting epidemiologic studies of patients (Table 2) exposed to newer radiographic procedures with potentially high doses (e.g., certain types of fluoroscopically-guided procedures, repeated administration of radionuclides for cardiac screening, and repeated positron emission tomography for patients at low risk of developing cancer recurrence or metastasis). There may also be public health value in conducting dosimetry evaluation in patients to develop clinical protocols for optimizing dose levels for most of the examinations listed immediately above and for some additional common examinations (e.g., bone mineral densitometry).

For medical radiation and nuclear energy workers who received continuous exposure to radiation over long periods of time (Table 3), public health needs continue to be served with careful dose monitoring and radiation epidemiologic studies of those workers with the highest doses (e.g., medical radiation workers who perform fluoroscopically guided procedures and those who mix or administer radionuclides in medicine, plutonium workers, uranium miners, and nuclear power plant accident cleanup workers). Conducting such studies provides empirical evidence to ensure that radiation protection standards are adequate. One area of indeterminate risks is for commercial aircrew. Epidemiologic studies have not shown consistent radiation-related risks for aircrew (UNSCEAR 2006). However, dose and risk estimation should be carried out for astronauts because of their potential to receive much greater doses.

Radiation doses to populations exposed to atomic bombs in warfare (Cullings et al. 2006; Egbert 2012), releases from nuclear accidents (Bouville et al. 2006; Gilbert et al. 2006), or nuclear testing have been reconstructed (Beck et al. 2006; Simon et al. 2010) (Table 4). In more limited cases, the populations have been followed up to evaluate health risks. Such studies are inherently difficult to conduct due to the challenge of tracing persons exposed decades ago. This information, however, can provide insights into the best approaches for estimating doses if such events occur in the future and to determine the public health burden of disease from past and future events, as well as provide useful data for policy recommendations about dose mitigation strategies.

The ubiquity of exposure to natural sources of radiation motivates the public health value of estimating doses for most of these populations, but the low level of radiation exposures complicates efforts to undertake epidemiologic studies (Table 1) (Hendry et al. 2009; Kendall et al. 2011). One important exception has been the completed epidemiologic studies of lung cancer associated with residential radon exposure (Field et al. 2006; WHO 2009).

Back to Top | Article Outline

Clinical importance of epidemiologic studies of radiation-exposed populations

There are at least three important reasons from the clinical perspective for studying radiation-exposed populations. The first is in common with all radiation protection-based studies; i.e., to ensure that a net benefit in health is achieved by the process of acquiring diagnostic information using ionizing radiation. A second reason is for clinical monitoring of persons who are at high risk of developing serious diseases for which early diagnosis or treatment can improve survival and/or quality of life. The third reason is to provide the scientific basis for educating physicians to enable them to counsel their patients about health risks associated with radiation exposures and for incorporating evidence-based justifications for ordering radiologic imaging procedures more fully in their medical practice.

For patients who have undergone radiation treatments via brachytherapy or external beam radiotherapy, follow-up studies are useful to ascertain acute and long-term health effects (the latter including second cancers and adverse functional effects due to tissue damage to critical organs such as the heart, lungs, thyroid, rectum, or other anatomic sites) (Table 2). In general, physicians need to learn more about the value of lifetime monitoring of their patients for late effects from radiotherapy. Patients undergoing one or more fluoroscopically guided interventional procedures should be evaluated for evidence of both early and late deterministic effects, such as tissue damage, and they should receive as much detailed dose information as possible about the need for repeated procedures of this type for chronic health conditions (Table 2). Appropriate information should be conveyed to primary care physicians about the need to maintain appropriate distances between family members and friends of those patients who have undergone thyroid ablation with 131I. Physicians also need to receive updated information about radiation doses and health risks to children and adolescents who are prescribed CT examinations. They also need to be familiar with the results of randomized trials of alternative approaches for evaluation of patients following head injury (Kuppermann et al. 2009), alternative approaches to CT for monitoring patients at increased risk of radiation-related second tumors (de Graaf et al. 2012), the American College of Radiology Appropriateness Criteria for choosing the appropriate type of imaging examination (Cascade 2000), and other strategies to incorporate an evidence-based approach that are particularly important when using repeated higher-dose imaging procedures to monitor patients with chronic diseases (Voss et al. 2009; Linet et al. 2012).

Clinicians should incorporate assessment of their patients’ job history to identify those with potentially serious exposures to ionizing radiation. Medical radiation workers (particularly those first employed prior to 1960, those performing or assisting with fluoroscopically guided procedures, and those mixing or handling radionuclides), as well as other medical professionals repeatedly involved in conducting fluoroscopic examinations, should be monitored for radiation-related health outcomes. These include certain types of cancer (thyroid cancer, breast cancer in women, brain tumors, and leukemia), nonmalignant thyroid diseases, circulatory diseases, and cataracts (Table 2). Underground miners (particularly those mining uranium, rare earths, coal, gold, and phosphates) should be monitored for lung cancer.

In the context of environmental exposures (Table 4), with a few exceptions, the evidence for significant health risks is generally weak. Some exceptions to this are Chernobyl residents living in proximity to the nuclear plant at the time of the accident (Cardis and Hatch 2011), Japanese atomic bomb survivors (Ozasa et al. 2012), persons living in proximity to nuclear testing sites (Lyon et al. 2006; Land et al. 2008), and residents living near the Techa River in the southern Ural mountains (Schonfeld et al. 2013). Where environmental exposures have a higher probability of inducing a cancer (e.g., for exposure to radon), physicians should encourage their patients to have their homes tested (Table 1).

Back to Top | Article Outline

Societal and public concern as motivators for undertaking epidemiologic studies of radiation-exposed populations

Public health and clinical considerations serve as the key motivators that determine whether an ongoing epidemiologic study of radiation-exposed populations should be continued or a new study launched, though sometimes the major rationale for a new study is societal or public concern. Most of the examples of radiation exposures in this category are included in the list in Table 4 primarily because the public is most concerned about exposures that are perceived as “involuntary.” The general public considers the great benefit of most diagnostic imaging and therapeutic procedures involving radiation to greatly outweigh the small risk. For workers in occupations involving exposure to radiation, the public considers those workers to have voluntarily chosen to work in such jobs. Ubiquitous natural background exposures are considered to be unavoidable or, through voluntary radon testing, the resident can identify and then mitigate such exposures.

In contrast, the general public has no control over nuclear accidents, nuclear testing, use of radiation for military or wartime purposes, or exposure to radiation at airports for security purposes. Although choosing to live near a nuclear plant can be argued to be voluntary, the construction of a new nuclear plant near one’s residence would be considered “involuntary.” These types of exposures have generated strong community pressure to undertake epidemiologic studies to evaluate health risks of sources noted in Table 4.

Back to Top | Article Outline

How to quantify health risks in radiation-exposed populations

Epidemiologic studies

The basis of most of our understanding of quantitative health risks of radiation in humans derives primarily from epidemiologic studies. Descriptive epidemiologic studies examine the occurrence and distribution of disease in populations, while analytic epidemiologic studies assess the statistical relationship between an exposure and a disease outcome.

Two attributes of exposed populations worthy of mention in relation to assessing feasibility of conducting new studies are average population dose and number of subjects available for study (Land 1980; Brenner et al. 2003). These attributes are important because of the inherent difficulties in assessing causal relationships (e.g., between disease endpoints and radiation exposure) in the presence of confounding variables. While data is limited in many cases on absolute population sizes and average doses received, Tables 14 present a qualitative assessment of these variables and our general assessment of the feasibility of studying a variety of potentially exposed populations.

A small proportion of the epidemiologic studies evaluating the relationship between radiation exposure and disease outcomes have used the ecological approach, in which the population rather than individuals is the primary unit evaluated. Examples of ecological studies of radiation exposures include investigations of natural background gamma radiation (Evrard et al. 2006) and radon exposures (Evrard et al. 2005) in relation to childhood leukemia and exposures to fallout from the Chernobyl nuclear reactor accident and risk of thyroid cancer risk in populations residing in regions within Ukraine (Jacob et al. 2006). Ecological studies can often be carried out quickly and inexpensively and are helpful if they suggest strong statistical associations, but the lack of information available on individuals may lead to false results.

The two major types of analytic observational epidemiologic studies are case-control studies and cohort studies. The case-control study design is used widely and compares the frequency of past occurrence of a given exposure or other attribute between cases of persons with a disease and a comparison group of persons without that disease. If a larger proportion of cases than the proportion of the comparison group have been exposed to a specific form of radiation, this statistical association may suggest an etiologic relationship. Examples of important case-control studies of radiation exposure include assessment of the risks of leukemia, non-Hodgkin lymphoma, and multiple myeloma in relation to diagnostic x-ray exposures in a U.S. health maintenance organization (Boice et al. 1991) and a nested case-control study of chronic lymphocytic leukemia and other forms of leukemia in relation to occupational exposure to radiation among Chernobyl cleanup workers in Ukraine (Zablotska et al. 2013).

In the cohort study design, an exposed population is followed up prospectively or retrospectively, and incidence and/or mortality from specific outcomes are compared with occurrence in an unexposed population followed up in a similar fashion. Examples of key cohort studies of radiation exposure include follow-up to assess incidence of solid tumors in relation to exposures from the atomic bombings among the Japanese atomic-bomb survivors (Preston et al. 2007), thyroid cancer in relation to fallout exposure among young persons residing in Ukraine in proximity to Chernobyl at the time of the accident (Tronko et al. 2006), and incidence of leukemia and brain tumors in relation to CT scans during childhood and adolescence among persons living in the United Kingdom (Pearce et al. 2012).

Increasingly important approaches for clarifying results of multiple epidemiologic studies of a given relationship are meta-analysis and pooled analysis. Meta-analysis involves use of statistical methods to compare and combine results of published data from different studies to reveal patterns, sources of variation, and other relationships. Meta-analysis, which requires only the published reports from studies, often accompanies a systematic review of studies on a given topic. Examples of important meta-analyses of radiation epidemiologic studies include assessment of lung cancer mortality from residential radon exposure (Lubin and Boice 1997) and examination of radiation-related circulatory disease risks (Little et al. 2012). Pooled analysis involves combining primary data from individual subjects across studies and requires common definitions, coding, and cut-points for variables and adjustment for the same confounders. An example of a well known pooled analysis of radiation epidemiologic studies is the 15-country study of cancer risks in nuclear industry workers (Cardis et al. 2007).

Back to Top | Article Outline

Risk projection studies

When risks to individuals from radiation are small, it may be difficult to study such risks directly. If the radiation exposure is common in the population, even small risks on an individual level can have a substantial public health impact. Methods and statistical models have been developed to estimate future cancer risks from low-dose radiation exposures (UNSCEAR 2000; NA/NRC 2006). Risk projection models use the extensive existing information on long-term cancer risks following radiation exposure to provide a timely and cost-effective estimate of the magnitude of the cancer or disease burden.

Examples of risk projection studies are numerous and include most all sources of exposure. For example, risks have been projected for medical imaging (Linet et al. 2012), for cancers in the United States that can be related to diagnostic x-rays and CT scans (Berrington de Gonzalez et al. 2009), and CT scans in children under 15 y of age (Miglioretti et al. 2013). From environmental exposures, the risks have been projected for exposures to radon (Pawel and Puskin 2004) and those due to exposure to nuclear testing fallout [e.g., for the residents of the Marshall Islands (Land et al. 2010) and those downwind of the Nevada Test Site (NA/NRC 1999)]. For occupational exposures, radiation-related health risks to astronauts have been projected (Cucinotta and Durante 2006). Software exists to project the potential magnitude of radiation-related cancer risks following low-dose radiation exposures based on dose, age at exposure, and age at disease expression (Berrington de Gonzalez et al. 2012).

Back to Top | Article Outline

Experimental studies

Questions about health risks associated with radiation exposure that require experimental manipulation can be addressed in animal studies. For example, the relation between the precise timing of a radiation exposure in relation to gestational period and a specific health outcome would be very difficult to study in observational studies in humans. A body of work in various animal models has identified excess risks of various tumors after in utero radiation (NCRP 2013). Investigations of very low dose and low dose-rate effects may be hampered by limited statistical power at low cumulative radiation doses. Results for rare outcomes from individual large and pooled studies may provide risk estimates, albeit with wide confidence intervals, but understanding of the shape of the dose-response relationship and of mechanisms of radiation pathogenesis will require research on radiobiological effects (Dauer et al. 2010).

Back to Top | Article Outline


Herein, many of the populations known and often assumed to be exposed to ionizing radiation have been identified, along with their unique attributes. Many of the populations are identified by proximity to the radiation source, while in fewer instances populations are identified by personnel monitoring data or empirical measurements on individuals. For the purposes of designing health risk studies, it is important to identify the target population whose members would have likely been exposed and to understand the extent to which radiation exposure can be estimated reliably, the variation in the radiation exposure of the population, the size of the target population in relation to statistical power requirements, and other key methodological features related to the potential for conducting a high-quality epidemiologic study. Determination of the priority for epidemiologic studies is also strongly related to the public health value, clinical appropriateness, and societal and public concerns about the radiation exposure of a population.

In this discussion, exposed populations have been categorized according to the sources or circumstances of their exposure (i.e., from naturally occurring radiation; as patients intentionally exposed for beneficial medical purposes; as workers who receive exposure in the course of occupations; and due to the combined circumstances of national security, warfare, nuclear testing, and military activities). While there may be further unidentified exposed populations, one of these categories will likely apply to the source or circumstance.

As presented in a series of tables, attributes of the exposed populations are important to take into account when considering or designing new epidemiologic studies. Quantifying these attributes is based on a degree of subjectivity but is still useful in the study of these populations. The following four attributes are particularly important:

  1. Population size adequate to meet statistical power considerations (Land 1980; Brenner et al. 2003);
  2. Large enough average dose and a wide enough dose range to derive a dose-response relationship;
  3. Understanding and capability to determine or reliably estimate individual doses—usually required for specific organs (Simon et al. 2006a); and
  4. Potential value of the study as determined by public health, clinical, or societal concerns.

At least the first two of these attributes have a synergistic relationship; hence, no absolute numbers for either can be given in the absence of the other. The sum of these four attributes, while not necessarily requiring equal weighting, provides much of the information needed to assess the feasibility or the likelihood of a successful health risk study. These tables may be useful in consideration of future possible studies.

Despite the large number of radiation-exposed populations and accumulation of knowledge on radiation-related health risks in humans from decades of epidemiologic studies, gaps in understanding remain. Further understanding is needed of the specific types of cancer, circulatory diseases, and cataracts associated with cumulative radiation doses <200 mGy and, for those medical conditions statistically associated with low-dose radiation exposure, the pattern of the dose response. The attributable risk of radiation to occurrence of disease is not well quantified for radiation exposures at all dose levels for either individuals or populations, in part due to the absence of specific radiation molecular signatures and to lack of comprehensive data on how to transport estimation of disease risks across populations or population subgroups. Knowledge is not well developed on health risks associated with internal emitters, and much more work is needed to clarify health risks from a wide group of radionuclides. Health risks associated with a broad range of radiation exposures of children require additional study, as do studies of other sensitive populations (e.g., pregnant women). There is very limited information on health risks to patients associated with radiation from diagnostic and therapeutic radiation procedures of all types. Information is limited on estimates of organ doses and radiation-related health risks of medical radiation and other medical workers with protracted exposures to radiation sources, particularly for workers exposed to higher doses from fluoroscopically guided interventional procedures or administration of radionuclides for diagnostic or treatment purposes. Further work is needed to clarify radiation-related late health effects and dose-response for the broad range of workers in the nuclear energy industry. Although the lifespan study of Japanese atomic bomb survivors is continuing, data are limited on long-term health effects from an acute single dose exposure during childhood or adolescence. Similarly, while the dosimetry and health risks studies of young persons living near Chernobyl and of the Chernobyl cleanup workers have been extensive, questions remain about long-term health effects for persons in these populations. A small number of populations and persons with genetically mediated radiation sensitivity have been identified, but the mechanisms of this sensitivity are not all understood. Genetic variants that may be linked with small risks have not been identified, although it is hypothesized that such variants might be important in explaining risks in general populations.

In summary, studies of radiation-exposed populations are a fundamental responsibility of a society that, by design, uses ionizing radiation in technological applications designed to either improve or better living conditions, health, or security. The individual and societal benefits derived from the use of radiation in medical diagnostic and therapeutic procedures, energy production and numerous other technologies must be weighed in relation to the possibility of causing adverse health effects. The need for society to make these comparisons is served by epidemiologic studies from which the risks can be deduced and compared to the benefits.

Back to Top | Article Outline


This work was supported by the Intramural Research Program of the National Cancer Institute, National Institutes of Health.

Back to Top | Article Outline


Ainsbury EA, Bouffler SD, Dorr W, Graw J, Muirhead CR, Edwards AA, Cooper J. Radiation cataractogenesis: a review of recent studies. Radiat Res 172: 1–9; 2009.
Allan JM. Genetic susceptibility to radiogenic cancer in humans. Health Phys 95: 677–686; 2008.
Beck HL, Anspaugh LR, Bouville A, Simon SL. Review of methods of dose estimation for epidemiological studies of the radiological impact of Nevada Test Site and global fallout. Radiat Res 166: 209–218; 2006.
Berrington de Gonzalez A, Mahesh M, Kim KP, Bhargavan M, Lewis R, Mettler F, Land C. Projected cancer risks from computed tomographic scans performed in the united states in 2007. Arch Intern Med 169: 2071–2077; 2009.
Berrington de Gonzalez A, Iulian Apostoaei A, Veiga LH, Rajaraman P, Thomas BA, Owen Hoffman F, Gilbert E, Land C. RadRAT: a radiation risk assessment tool for lifetime cancer risk projection. J Radiol Prot 32: 205–222; 2012.
Boice JD Jr. Ionizing radiation. In: Schottenfeld D, Fraumeni JF Jr, eds. Cancer epidemiology and prevention. New York: Oxford University Press; 2006: 259–293.
Boice JD Jr, Morin MM, Glass AG, Friedman GD, Stovall M, Hoover RN, Fraumeni JF Jr. Diagnostic x-ray procedures and risk of leukemia, lymphoma, and multiple myeloma. JAMA 265: 1290–1294; 1991.
Bouville A, Chumak VV, Inskip PD, Kryuchkov V, Luckyanov N. The chornobyl accident: estimation of radiation doses received by the Baltic and Ukrainian cleanup workers. Radiat Res 166: 158–167; 2006.
Brenner DJ, Doll R, Goodhead DT, Hall EJ, Land CE, Little JB, Lubin JH, Preston DL, Preston RJ, Puskin JS, Ron E, Sachs RK, Samet JM, Setlow RB, Zaider M. Cancer risks attributable to low doses of ionizing radiation: assessing what we really know. Proc Nat Acad Sci USA 100: 13761–13766; 2003.
Cardis E, Hatch M. The Chernobyl accident—an epidemiological perspective. Clin Oncol (R Coll Radiol) 23: 251–260; 2011.
Cardis E, Kesminiene A, Ivanov V, Malakhova I, Shibata Y, Khrouch V, Drozdovitch V, Maceika E, Zvonova I, Vlassov O, Bouville A, Goulko G, Hoshi M, Abrosimov A, Anoshko J, Astakhova L, Chekin S, Demidchik E, Galanti R, Ito M, Korobova E, Lushnikov E, Maksioutov M, Masyakin V, Nerovnia A, Parshin V, Parshkov E, Piliptsevich N, Pinchera A, Polyakov S, Shabeka N, Suonio E, Tenet V, Tsyb A, Yamashita S, Williams D. Risk of thyroid cancer after exposure to 131I in childhood. J Nat Cancer Inst 97: 724–732; 2005.
Cardis E, Vrijheid M, Blettner M, Gilbert E, Hakama M, Hill C, Howe G, Kaldor J, Muirhead CR, Schubauer-Berigan M, Yoshimura T, Bermann F, Cowper G, Fix J, Hacker C, Heinmiller B, Marshall M, Thierry-Chef I, Utterback D, Ahn YO, Amoros E, Ashmore P, Auvinen A, Bae JM, Bernar J, Biau A, Combalot E, Deboodt P, Diez Sacristan A, Eklof M, Engels H, Engholm G, Gulis G, Habib RR, Holan K, Hyvonen H, Kerekes A, Kurtinaitis J, Malker H, Martuzzi M, Mastauskas A, Monnet A, Moser M, Pearce MS, Richardson DB, Rodriguez-Artalejo F, Rogel A, Tardy H, Telle-Lamberton M, Turai I, Usel M, Veress K. The 15-country collaborative study of cancer risk among radiation workers in the nuclear industry: estimates of radiation-related cancer risks. Radiat Res 167: 396–416; 2007.
Cascade PN. The American College of Radiology. ACR appropriateness criteria project. Radiol 214 (Suppl): 3–46; 2000.
Cucinotta FA, Durante M. Cancer risk from exposure to galactic cosmic rays: implications for space exploration by human beings. Lancet Oncol 7: 431–435; 2006.
Cullings HM, Fujita S, Funamoto S, Grant EJ, Kerr GD, Preston DL. Dose estimation for atomic bomb survivor studies: its evolution and present status. Radiat Res 166: 219–254; 2006.
Darby SC, Ewertz M, McGale P, Bennet AM, Blom-Goldman U, Bronnum D, Correa C, Cutter D, Gagliardi G, Gigante B, Jensen MB, Nisbet A, Peto R, Rahimi K, Taylor C, Hall P. Risk of ischemic heart disease in women after radiotherapy for breast cancer. New Engl J Med 368: 987–998; 2013.
Dauer LT, Brooks AL, Hoel DG, Morgan WF, Stram D, Tran P. Review and evaluation of updated research on the health effects associated with low-dose ionising radiation. Radiat Protect Dosim 140: 103–136; 2010.
de Graaf P, Goricke S, Rodjan F, Galluzzi P, Maeder P, Castelijns JA, Brisse HJ. Guidelines for imaging retinoblastoma: imaging principles and MRI standardization. Pediatr Radiol 42: 2–14; 2012.
Dupont P, Besson MT, Devaux J, Lievens JC. Reducing canonical Wingless/Wnt signaling pathway confers protection against mutant Huntingtin toxicity in Drosophila. Neurobiol Disease 47: 237–247; 2012.
Egawa H, Furukawa K, Preston D, Funamoto S, Yonehara S, Matsuo T, Tokuoka S, Suyama A, Ozasa K, Kodama K, Mabuchi K. Radiation and smoking effects on lung cancer incidence by histological types among atomic bomb survivors. Radiat Res 178: 191–201; 2012.
Egbert SD. The 2002 dosimetry system (DS02) and available fluences for organ dose calculations. Radiat Protect Dosim 149: 21–27; 2012.
Evrard AS, Hemon D, Billon S, Laurier D, Jougla E, Tirmarche M, Clavel J. Ecological association between indoor radon concentration and childhood leukaemia incidence in France, 1990–1998. Eur J Cancer Prev 14: 147–157; 2005.
Evrard AS, Hemon D, Billon S, Laurier D, Jougla E, Tirmarche M, Clavel J. Childhood leukemia incidence and exposure to indoor radon, terrestrial and cosmic gamma radiation. Health Phys 90: 569–579; 2006.
Field RW, Krewski D, Lubin JH, Zielinski JM, Alavanja M, Catalan VS, Klotz JB, Letourneau EG, Lynch CF, Lyon JL, Sandler DP, Schoenberg JB, Steck DJ, Stolwijk JA, Weinberg C, Wilcox HB. An overview of the North American residential radon and lung cancer case-control studies. J Toxicol Environm Health A 69: 599–631; 2006.
Frieben A. Demonstration eines cancroids des rechten handruckens, das sich nach langdauernder einwirkung von rontgenstrahlen entwickelt hatte. Fortsch Roentgenstr 6: 106–111; 1902 (in German).
Furukawa K, Preston DL, Lonn S, Funamoto S, Yonehara S, Matsuo T, Egawa H, Tokuoka S, Ozasa K, Kasagi F, Kodama K, Mabuchi K. Radiation and smoking effects on lung cancer incidence among atomic bomb survivors. Radiat Res 174: 72–82; 2010.
Gilbert ES, Thierry-Chef I, Cardis E, Fix JJ, Marshall M. External dose estimation for nuclear worker studies. Radiat Res 166: 168–173; 2006.
Hendry JH, Simon SL, Wojcik A, Sohrabi M, Burkart W, Cardis E, Laurier D, Tirmarche M, Hayata I. Human exposure to high natural background radiation: what can it teach us about radiation risks? J Radiol Prot 29: A29–A42; 2009.
Hymes SR, Strom EA, Fife C. Radiation dermatitis: clinical presentation, pathophysiology, and treatment 2006. J Am Acad Dermatol 54: 28–46; 2006.
Ichimaru M, Ishimaru T, Tsuchimoto T, Kirshbaum JD. Incidence of aplastic anemia in a-bomb survivors. Hiroshima and Nagasaki, 1946–1967. Radiat Res 49: 461–472; 1972.
International Commission on Radiological Protection. Biological effects after prenatal irradiation (embryo and fetus). New York: Elsevier; Publication 90, Ann. ICRP 33(1–2); 2003.
International Commission on Radiation Units and Measurements. Radiation quantities and units. Oxford, UK: Oxford University Press; Report 33; 1980.
International Commission on Units and Measurements. Retrospective assessment of exposure to ionising radiation. Oxford, UK: Oxford University Press; Report 68; 2002.
Iwanaga M, Hsu WL, Soda M, Takasaki Y, Tawara M, Joh T, Amenomori T, Yamamura M, Yoshida Y, Koba T, Miyazaki Y, Matsuo T, Preston DL, Suyama A, Kodama K, Tomonaga M. Risk of myelodysplastic syndromes in people exposed to ionizing radiation: a retrospective cohort study of Nagasaki atomic bomb survivors. J Clin Oncol 29: 428–434; 2011.
Jacob P, Bogdanova TI, Buglova E, Chepurniy M, Demidchik Y, Gavrilin Y, Kenigsberg J, Meckbach R, Schotola C, Shinkarev S, Tronko MD, Ulanovsky A, Vavilov S, Walsh L. Thyroid cancer risk in areas of Ukraine and Belarus affected by the Chernobyl accident. Radiat Res 165: 1–3; 2006.
Karagas MR, Nelson HH, Zens MS, Linet M, Stukel TA, Spencer S, Applebaum KM, Mott L, Mabuchi K. Squamous cell and basal cell carcinoma of the skin in relation to radiation therapy and potential modification of risk by sun exposure. Epidemiol 18: 776–784; 2007.
Kendall G, Little MP, Wakeford R. Numbers and proportions of leukemias in young people and adults induced by radiation of natural origin. Leukemia Res 35: 1039–1043; 2011.
Kleinerman RA. Radiation-sensitive genetically susceptible pediatric sub-populations. Pediatric Radiol 39 (Suppl 1): S27–S31; 2009.
Kuppermann N, Holmes JF, Dayan PS, Hoyle JD Jr, Atabaki SM, Holubkov R, Nadel FM, Monroe D, Stanley RM, Borgialli DA, Badawy MK, Schunk JE, Quayle KS, Mahajan P, Lichenstein R, Lillis KA, Tunik MG, Jacobs ES, Callahan JM, Gorelick MH, Glass TF, Lee LK, Bachman MC, Cooper A, Powell EC, Gerardi MJ, Melville KA, Muizelaar JP, Wisner DH, Zuspan SJ, Dean JM, Wootton-Gorges SL. Identification of children at very low risk of clinically-important brain injuries after head trauma: a prospective cohort study. Lancet 374: 1160–1170; 2009.
Land CE. Estimating cancer risks from low doses of ionizing radiation. Science 209: 1197–1203; 1980.
Land CE, Zhumadilov Z, Gusev BI, Hartshorne MH, Wiest PW, Woodward PW, Crooks LA, Luckyanov NK, Fillmore CM, Carr Z, Abisheva G, Beck HL, Bouville A, Langer J, Weinstock R, Gordeev KI, Shinkarev S, Simon SL. Ultrasound-detected thyroid nodule prevalence and radiation dose from fallout. Radiat Res 169: 373–383; 2008.
Land CE, Bouville A, Apostoaei I, Simon SL. Projected lifetime cancer risks from exposure to regional radioactive fallout in the Marshall Islands. Health Phys 99: 201–215; 2010.
Linet MS, Slovis TL, Miller DL, Kleinerman R, Lee C, Rajaraman P, Berrington de Gonzalez A. Cancer risks associated with external radiation from diagnostic imaging procedures. CA Cancer J Clinicians 62(2):75–100; 2012.
Little MP, Azizova TV, Bazyka D, Bouffler SD, Cardis E, Chekin S, Chumak VV, Cucinotta FA, de Vathaire F, Hall P, Harrison JD, Hildebrandt G, Ivanov V, Kashcheev VV, Klymenko SV, Kreuzer M, Laurent O, Ozasa K, Schneider T, Tapio S, Taylor AM, Tzoulaki I, Vandoolaeghe WL, Wakeford R, Zablotska LB, Zhang W, Lipshultz SE. Systematic review and meta-analysis of circulatory disease from exposure to low-level ionizing radiation and estimates of potential population mortality risks. Environm Health Persp 120: 1503–1511; 2012.
Little MP, Goodhead DT, Bridges BA, Bouffler SD. Evidence relevant to untargeted and transgenerational effects in the offspring of irradiated parents. Mutat Res pii:S1383-5742(13)00047-1; 2013. doi: 10.1016/j.mrrev.2013.04.001.
Lubin JH, Boice JD Jr. Lung cancer risk from residential radon: meta-analysis of eight epidemiologic studies. J Nat Cancer Inst 89: 49–57; 1997.
Lyon JL, Alder SC, Stone MB, Scholl A, Reading JC, Holubkov R, Sheng X, White GL Jr, Hegmann KT, Anspaugh L, Hoffman FO, Simon SL, Thomas B, Carroll R, Meikle AW. Thyroid disease associated with exposure to the Nevada Nuclear Weapons Test Site radiation: a reevaluation based on corrected dosimetry and examination data. Epidemiol 17: 604–614; 2006.
Miglioretti DL, Johnson E, Williams A, Greenlee RT, Weinmann S, Solberg LI, Feigelson HS, Roblin D, Flynn MJ, Vanneman N, Smith-Bindman R. The use of computed tomography in pediatrics and the associated radiation exposure and estimated cancer risk. JAMA Pediatr 167(8):700–707; 2013.
National Academies/Natural Research Council. Exposure of the american people to iodine-131 from Nevada nuclear-bomb tests: review of the National Cancer Institute report and public health implications. Washington, DC: National Academies Press; 1999.
National Academies/Natural Research Council. Committee to assess health risks from exposure to low levels of ionizing radiation. Health risks from exposure to low levels of ionizing radiation. BEIR VII. Washington, DC: National Academies Press; 2006.
NCRP. Ionizing radiation exposure of the population of the United States. Bethesda, MD: National Council on Radiation Protection and Measurements; NCRP Report No. 160; 2009.
NCRP. Radiation dose and the impacts on exposed populations. Proceedings of the Forty-ninth Annual Meeting. Health Phys 106 (2): 145–339; 2013.
Neglia JP, Robison LL, Stovall M, Liu Y, Packer RJ, Hammond S, Yasui Y, Kasper CE, Mertens AC, Donaldson SS, Meadows AT, Inskip PD. New primary neoplasms of the central nervous system in survivors of childhood cancer: a report from the childhood cancer survivor study. J Nat Cancer Inst 98: 1528–1537; 2006.
Ozasa K, Shimizu Y, Suyama A, Kasagi F, Soda M, Grant EJ, Sakata R, Sugiyama H, Kodama K. Studies of the mortality of atomic bomb survivors, report 14, 1950–2003: an overview of cancer and noncancer diseases. Radiat Res 177: 229–243; 2012.
Pawel DJ, Puskin JS. The U.S. Environmental Protection Agency’s assessment of risks from indoor radon. Health Phys 87: 68–74; 2004.
Pearce MS, Salotti JA, Little MP, McHugh K, Lee C, Kim KP, Howe NL, Ronckers CM, Rajaraman P, Sir Craft AW, Parker L, Berrington de Gonzalez A. Radiation exposure from CT scans in childhood and subsequent risk of leukaemia and brain tumours: a retrospective cohort study. Lancet 380: 499–505; 2012.
Preston DL, Ron E, Tokuoka S, Funamoto S, Nishi N, Soda M, Mabuchi K, Kodama K. Solid cancer incidence in atomic bomb survivors: 1958–1998. Radiat Res 168: 1–64; 2007.
Ronckers CM, Doody MM, Lonstein JE, Stovall M, Land CE. Multiple diagnostic x-rays for spine deformities and risk of breast cancer. Cancer Epidemiol Biomarkers Prev 17: 605–613; 2008.
Schonfeld SJ, Krestinina LY, Epifanova S, Degteva MO, Akleyev AV, Preston DL. Solid cancer mortality in the Techa River cohort (1950–2007). Radiat Res 179: 183–189; 2013.
Scott SG. Notes on a case of x-ray dermatitis with fatal termination. Arch Roentgen Ray 15: 443–444; 1911.
Simon SL, Kleinerman RA, Ron E, Bouville A. Uses of dosimetry in radiation epidemiology. Radiat Res 166: 125–127; 2006a.
Simon SL, Bouville A, Land C. Fallout from nuclear weapons tests and cancer risk. American Scientist 91: 48–57; 2006b.
Simon SL, Bouville A, Land CE, Beck HL. Radiation doses and cancer risks in the Marshall Islands associated with exposure to radioactive fallout from Bikini and Enewetak nuclear weapons tests: summary. Health Phys 99: 105–123; 2010.
Travis LB, Hill DA, Dores GM, Gospodarowicz M, van Leeuwen FE, Holowaty E, Glimelius B, Andersson M, Wiklund T, Lynch CF, Van’t Veer MB, Glimelius I, Storm H, Pukkala E, Stovall M, Curtis R, Boice JD Jr, Gilbert E. Breast cancer following radiotherapy and chemotherapy among young women with Hodgkin disease. JAMA 290: 465–475; 2003.
Tronko MD, Howe GR, Bogdanova TI, Bouville AC, Epstein OV, Brill AB, Likhtarev IA, Fink DJ, Markov VV, Greenebaum E, Olijnyk VA, Masnyk IJ, Shpak VM, McConnell RJ, Tereshchenko VP, Robbins J, Zvinchuk OV, Zablotska LB, Hatch M, Luckyanov NK, Ron E, Thomas TL, Voilleque PG, Beebe GW. A cohort study of thyroid cancer and other thyroid diseases after the Chornobyl accident: thyroid cancer in Ukraine detected during first screening. J Nat Cancer Inst 98: 897–903; 2006.
UNSCEAR. Sources and effects of ionizing radiation, Vol. I. New York: United Nations Scientific Committee on the Effects of Atomic Radiation; 1988.
UNSCEAR. Sources and effects of ionizing radiation. New York: United Nations Scientific Committee on the Effects of Atomic Radiation; United Nations Publ No E.94.IX.11. Annex A; United Nations Publ No E.94.IX.11. Annex A; 1994.
UNSCEAR. Sources and effects of ionizing radiation. Vol. I. New York: United Nations Scientific Committee on the Effects of Atomic Radiation; 2000.
UNSCEAR. effects of ionizing radiation, Vol. I. New York: United Nations Scientific Committee on the Effects of Atomic Radiation; 2006.
UNSCEAR. Sources and effects of ionizing radiation, Vol. I. New York: United Nations Scientific Committee on the Effects of Atomic Radiation; 2008.
UNSCEAR. Biological mechanisms of radiation actions at low doses. New York: United Nations Scientific Committee on the Effects of Atomic Radiation; 2012.
Voss SD, Reaman GH, Kaste SC, Slovis TL. The ALARA concept in pediatric oncology. Pediatric Radiol 39: 1142–1146; 2009.
Wakeford R. Radiation in the workplace - a review of studies of the risks of occupational exposure to ionising radiation. J Radiol Protect 29: A61–A79; 2009.
WHO. WHO handbook on indoor radon: a public health perspective. Geneva: World Health Organization; 2009.
Zablotska LB, Bazyka D, Lubin JH, Gudzenko N, Little MP, Hatch M, Finch S, Dyagil I, Reiss RF, Chumak VV, Bouville A, Drozdovitch V, Kryuchkov VP, Golovanov I, Bakhanova E, Babkina N, Lubarets T, Bebeshko V, Romanenko A, Mabuchi K. Radiation and the risk of chronic lymphocytic and other leukemias among Chornobyl cleanup workers. Environ Health Persp 121: 59–65; 2013.

epidemiology; exposure, occupational; medical radiation; National Council on Radiation Protection and Measurements

Supplemental Digital Content

Back to Top | Article Outline
© 2014 by the Health Physics Society