Intended for healthcare professionals


Risk of cancer after low doses of ionising radiation: retrospective cohort study in 15 countries

BMJ 2005; 331 doi: (Published 07 July 2005) Cite this as: BMJ 2005;331:77
  1. E Cardis, head of radiation group1 (cardis{at},
  2. M Vrijheid, scientist1,
  3. M Blettner, professor2,
  4. E Gilbert, expert3,
  5. M Hakama, research professor4,
  6. C Hill, epidemiologist5,
  7. G Howe, professor of epidemiology6,
  8. J Kaldor, deputy director7,
  9. C R Muirhead, group leader epidemiology8,
  10. M Schubauer-Berigan, senior research epidemiologist, industrywide studies branch9,
  11. T Yoshimura, director10,
  12. F Bermann, medical counsellor11,
  13. G Cowper, consultant to IARC12,
  14. J Fix, staff scientist13,
  15. C Hacker, health physicist14,
  16. B Heinmiller, senior scientist15,
  17. M Marshall, consultant to IARC on radiation dosimetry16,
  18. I Thierry-Chef, postdoctoral student1,
  19. D Utterback, chief, health-related energy research branch9,
  20. Y-O Ahn, professor17,
  21. E Amoros, research assistant18,
  22. P Ashmore, affiliate scientist at the McLaughlin Centre19,
  23. A Auvinen, research professor4,
  24. J-M Bae, associate professor20,
  25. J Bernar Solano, head of division of research21,
  26. A Biau, director of scientific and technical assessment22,
  27. E Combalot, research assistant1,
  28. P Deboodt, health physicist23,
  29. A Diez Sacristan, inspector24,
  30. M Eklof25,
  31. H Engels, nuclear inspector23,
  32. G Engholm, principal administrative officer26,
  33. G Gulis, associate professor27,
  34. R Habib, assistant professor28,
  35. K Holan, senior adviser29,
  36. H Hyvonen, managing director30,
  37. A Kerekes, head31,
  38. J Kurtinaitis, chief32,
  39. H Malker, research director33,
  40. M Martuzzi, technical officer34,
  41. A Mastauskas, head35,
  42. A Monnet, senior statistical programmer36,
  43. M Moser, chief37,
  44. M S Pearce, senior research associate38,
  45. D B Richardson, assistant professor39,
  46. F Rodriguez-Artalejo, professor of preventive medicine and public health40,
  47. A Rogel, epidemiologist41,
  48. H Tardy, research assistant1,
  49. M Telle-Lamberton, epidemiologist41,
  50. I Turai, head chief physician31,
  51. M Usel, research assistant42,
  52. K Veress, lecturer43
  1. 1 International Agency for Research on Cancer, Lyons, France
  2. 2 Institute of Medical Biostatistics, Epidemiology and Informatics, University of Mainz, Germany
  3. 3 Radiation Epidemiology Branch, Division of Epidemiology and Genetics, National Cancer Institute, Bethesda, MD, USA
  4. 4 University of Tampere, Tampere, Finland
  5. 5 Institut Gustave-Roussy, Villejuif, France
  6. 6 Mailman School of Public Health, Columbia University, New York, USA
  7. 7 National Centre in HIV Epidemiology and Clinical Research, Sydney, NSW, Australia
  8. 8 Radiation Protection Division, Health Protection Agency, Chilton, Didcot, Oxfordshire
  9. 9 Division of Surveillance, Hazard Evaluations and Field Studies, National Institute for Occupational Safety and Health, Cincinnati, OH, USA
  10. 10 Fukuoka Institute of Health and Environmental Sciences, Fukuoka, Japan
  11. 11 Conseiller Médical du CEA, Paris, France
  12. 12 Atomic Energy Commission of Canada, Deep River, ON, Canada
  13. 13 Pacific Northwest National Laboratory, Richland, WA, USA
  14. 14 Safety and Radiation Science, Australian Nuclear Science and Technology Organisation, NSW, Australia
  15. 15 AECL Radiation Biology and Health Physics Branch, Chalk River Laboratories, Chalk, ON, Canada
  16. 16 Twin Trees, Blewbury, Didcot, Oxfordshire
  17. 17 Department of Preventive Medicine, Seoul National University College of Medicine, Seoul, Korea
  18. 18 Epidemiological Research and Surveillance Unit in Transport, Occupation and Environment; French National Institute for Transport and Safety Research (INRETS), Arcueil, France
  19. 19 Radiation Protection Bureau, Health Canada, Ottawa, Canada
  20. 20 Department of Preventive Medicine, Cheju National University College of Medicine, Cheju, Korea
  21. 21 AMYS, UNESA, Madrid, Spain
  22. 22 Institute of Radioprotection and Nuclear Security, DESTQ/DEAS, Le Vésinet, France
  23. 23 Nuclear Research Centre (SCK.CEN), Radiation Protection Division, Mol, Belgium
  24. 24 Operational Radiological Protection, Nuclear Safety Council, Spain
  25. 25 Statens Vattenfallsverk Forsmark, Osthammer, Sweden
  26. 26 Institute for East-European Studies, Uppsala University, Sweden
  27. 27 Department of Hygiene and Epidemiology, Faculty of Health Care and Social Work, Trnava University, Trnava, Slovak Republic
  28. 28 Faculty of Health Sciences, American University of Beirut, Lebanon
  29. 29 Slovenske Elektrárne, Bratislava, Slovak Republic
  30. 30 Doseco Ltd, Jyvaskyla, Finland
  31. 31 “Frederic Joliot-Curie” National Research Institute for Radiobiology and Radiohygiene of the “Fodor József” National Centre for Public Health, Budapest, Hungary
  32. 32 Lithuanian Cancer Registry, Vilnius University Oncology Institute, Vilnius, Lithuania
  33. 33 Vasternorrland County Council, Department of Research and Development, Sundsvall, Sweden
  34. 34 WHO European Centre for Environment and Health, Rome, Italy
  35. 35 Radiation Protection Centre, Vilnius, Lithuania
  36. 36 Serono International SA, Geneva, Switzerland
  37. 37 Physics and Biology Section, Radiation Protection Division, Federal Office of Public Health, Bern, Switzerland
  38. 38 School of Clinical Medical Sciences, University of Newcastle upon Tyne, Newcastle upon Tyne
  39. 39 Department of Epidemiology, School of Public Health, Chapel Hill, NC, USA
  40. 40 Department of Preventive Medicine and Public Health, School of Medicine, University Autonoma de Madrid, Spain
  41. 41 Laboratory of Epidemiology, Institute for Radiological Protection and Nuclear Safety, Fontenay-aux-Roses, France
  42. 42 Medical Inspectorate of Factories, Geneva, Switzerland
  43. 43 Institute of Public Health, Semmelweis University, Budapest, Hungary
  1. Correspondence to: E Cardis
  • Accepted 23 May 2005


Objectives To provide direct estimates of risk of cancer after protracted low doses of ionising radiation and to strengthen the scientific basis of radiation protection standards for environmental, occupational, and medical diagnostic exposures.

Design Multinational retrospective cohort study of cancer mortality.

Setting Cohorts of workers in the nuclear industry in 15 countries.

Participants 407 391 workers individually monitored for external radiation with a total follow-up of 5.2 million person years.

Main outcome measurements Estimates of excess relative risks per sievert (Sv) of radiation dose for mortality from cancers other than leukaemia and from leukaemia excluding chronic lymphocytic leukaemia, the main causes of death considered by radiation protection authorities.

Results The excess relative risk for cancers other than leukaemia was 0.97 per Sv, 95% confidence interval 0.14 to 1.97. Analyses of causes of death related or unrelated to smoking indicate that, although confounding by smoking may be present, it is unlikely to explain all of this increased risk. The excess relative risk for leukaemia excluding chronic lymphocytic leukaemia was 1.93 per Sv (< 0 to 8.47). On the basis of these estimates, 1-2% of deaths from cancer among workers in this cohort may be attributable to radiation.

Conclusions These estimates, from the largest study of nuclear workers ever conducted, are higher than, but statistically compatible with, the risk estimates used for current radiation protection standards. The results suggest that there is a small excess risk of cancer, even at the low doses and dose rates typically received by nuclear workers in this study.


Ionising radiation is one of the most studied and ubiquitous carcinogens in our environment. The main basis for radiation protection recommendations is the study of survivors of the Japanese atomic bomb (A bomb), a population exposed primarily at high dose rates.13 The primary public health concern, however, is the protection of people from relatively low dose, protracted or fractionated exposures such as those received by the public in the general environment, by patients through repeated diagnostic procedures,4 and by radiation workers.

The effects of low dose chronic exposure to external radiation have been directly estimated in several cohorts of workers in the nuclear industry,3 but the sample size has limited the precision of these estimates. Analyses of combined cohorts have improved precision.57 Estimates from these analyses, however, are compatible with a range of possibilities, from a reduction of risk at low doses to risks higher than those underlying current radiation protection recommendations.

The 15 country study, an international collaborative study of cancer risk among radiation workers in the nuclear industry, was carried out to further improve the precision of direct estimates of risk after protracted low dose exposures and to strengthen the scientific basis of radiation protection.1 We present risk estimates for mortality from all cancers, excluding leukaemia, and from leukaemia excluding chronic lymphocytic leukaemia and compare them with estimates derived from data on survivors of the A bomb. We have used the term nuclear industry to refer to facilities engaged in production of nuclear power, manufacture of nuclear weapons, enrichment and processing of nuclear fuel, production of radioisotopes, or reactor or weapons research. Uranium mining is not included.


This multinational retrospective cohort study used a common protocol in 15 countries and collected information on nearly 600 000 workers. Study cohorts were defined from employment or dosimetric records of participating facilities or, where available, from centralised national dose registries. The a priori eligibility criteria for inclusion of cohorts8 were essentially complete and non-selective follow-up for mortality; availability of individual annual recorded estimates of dose for all monitored workers; and availability of information on historical monitoring policies and practices. We included all workers who had been monitored for external photon (x and γ) radiation exposure through the use of personal dosimeters. Details of country specific methods are described elsewhere.9

Ascertainment of vital status and cause of death

We established vital status through linkage with national or regional death registries. In a few countries where this was not possible, appropriate records of local authorities were used. Completeness of follow-up ranged from 87% to nearly 100%. Vital statistics registries provided cause of death, which was known for over 90% of workers who died.

Adequacy of dosimetric records

We reconstructed each worker's dosimetric history using recorded doses from individual facilities or national dose registries. A study of errors in recorded doses evaluated the comparability of dose estimates across facilities and time and identified and quantified sources of bias and uncertainties.9 Doses from higher energy photons (100-3000 keV), which constituted most of the dose in most cohorts, were judged to have been measured in a comparable way over time and across facilities.9 10 The adequacy of practices and technology to measure and record dose from other radiation types (neutrons, internal exposures), however, varied substantially, particularly in earlier years. We therefore excluded workers with potential for substantial doses (≥ 10% of their whole body dose) from these radiation types.

Main study population

The main study population was defined as workers who had been employed in one or more facilities for at least one year (113 711 workers excluded), who had been monitored for external radiation exposure (38 521 workers excluded), and whose doses resulted predominantly from higher energy photon radiation (39 730 workers with internal contamination and 19 041 with neutron exposures excluded).

Dosimetric errors and derivation of organ doses

The major sources of errors in higher energy photon doses were dosimetry technology, exposure conditions, and calibration practices. Errors from these sources were quantified and bias factors specific to the doses to each organ of interest calculated for each model of dosimeter used and by type of facility (nuclear power plants and mixed activities facilities).11 12 Organ doses were derived by dividing recorded doses by the appropriate organ dose bias factor. We used doses to the colon and active bone marrow for analyses of mortality from all cancers excluding leukaemia and from leukaemia, respectively. All doses are expressed as dose equivalents in sieverts (Sv).

Statistical methods

Analyses were based on a linear relative risk Poisson regression model, in which the relative risk is of the form 1+βZ, where Z is the cumulative dose equivalent in Sv and β is the excess relative risk per Sv; 95% likelihood based confidence intervals were calculated. We used 11 a priori categories of dose (< 5, 5- < 10, 10- < 20, 20- < 50, 50- < 100, 100- < 150, 150- < 200, 200- < 300, 300- < 400, 400- < 500, ≥ 500 mSv). Analyses used only underlying cause of death. Estimates of excess relative risk were stratified for sex, age, and calendar period (both in five year categories), facility, duration of employment (< 10 years, ≥ 10 years), and socioeconomic status. In the analyses of all cancers we excluded cohorts for which socioeconomic information was unavailable or incomplete (Japan, Idaho National Engineering Laboratory (INEL), Ontario Hydro Canada), but we included them in analyses of leukaemia as the potential for confounding by socioeconomic status was thought to be less for leukaemia. To allow for a latent period between exposure and death, doses were lagged by two years for leukaemia and 10 years for other cancers, as in other studies of nuclear workers57 and assessments of radiation risk.1 2 Sensitivity analyses were conducted with a range of different lags. Attributable risks were estimated by multiplying the excess relative risks by the average dose in the cohort.

We have focused on the main causes of death for which radiation protection committees have provided risk estimates: all cancers excluding leukaemia and leukaemia excluding chronic lymphocytic leukaemia. Chronic lymphocytic leukaemia is excluded because it is thought to be less readily inducible by ionising radiation than other leukaemias.3 We have also presented risk estimates for solid cancers (that is, excluding lymphatic and haematopoietic malignancies) to compare with recent data for A bomb survivors13 and for all cancers excluding leukaemia, lung, and pleural cancers (which have the greatest potential for confounding by smoking, internally incorporated radionuclides, and other occupational carcinogens). We investigated confounding by smoking by separately analysing solid cancers related or unrelated to smoking and two groupings of smoking related outcomes other than cancer (all non-malignant respiratory diseases and chronic obstructive bronchitis and emphysema).

Analysis of data from survivors of A bomb

We analysed mortality data from the A bomb survivors for solid cancer to 199713 and leukaemia to 199014 using similar methods to provide risk estimates for comparison. Analyses were stratified for attained age, city, and calendar time and restricted to men aged 20-60 at exposure, the group most comparable to the workers.


Overall, 598 068 workers were employed in at least one of 154 facilities. Most facilities were involved in nuclear power production; the rest specialised in different activities, including research, waste management, and production of fuel, isotopes, and weapons. The main study population comprised 407 391 workers (table 1). A total of 24 158 (5.9%) people were known to have died during the study period: 6519 from cancers other than leukaemia and 196 from leukaemia excluding chronic lymphocytic leukaemia. The total duration of follow-up was 5 192 710 person years and the total collective recorded dose was 7892 Sv. Most workers in the study were men (90%), and men received 98% of the collective dose. The overall average cumulative recorded dose was 19.4 mSv. The distribution of recorded doses was skewed (fig 1). Ninety per cent of workers received cumulative doses < 50 mSv and less than 0.1% received cumulative doses > 500 mSv.

Table 1.

Cohorts included in the 15 country study

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Fig 1
Fig 1

Distribution of cumulative radiation doses among workers included in the analyses

For all cancers excluding leukaemia, the excess relative risk was 0.97 per Sv and was significantly different from zero (95% confidence interval 0.14 to 1.97) (table 2). This estimate corresponds to a relative risk of 1.10 for a radiation dose of 100 mSv. For solid cancers, the excess relative risk was 0.87 (0.03 to 1.88), higher than but statistically compatible with the estimate for A bomb survivors (0.32 per Sv). The excess relative risk for leukaemia excluding chronic lymphocytic leukaemia was 1.93 per Sv (< 0 to 8.47), which gives a relative risk of 1.19 for a dose of 100 mSv. This estimate is between the linear and linear quadratic extrapolations from data on A bomb survivors (table 2).

Table 2.

Estimates of excess relative risk per Sv (95% confidence interval) for all cancers excluding leukaemia, solid cancers, and leukaemia excluding chronic lymphocytic leukaemia, for nuclear workers and survivors of A bomb in Japan *

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Table 3 assesses the possible confounding effect of smoking. Excess relative risks ranged between 0.59 per Sv (−0.29 to 1.70) for all cancers excluding leukaemia and lung and pleural cancer, and 0.91 per Sv (−0.11 to 2.21) for smoking related cancers.

Table 3.

Estimates of excess relative risk per Sv (95% confidence intervals) for specific causes of death

View this table:

The increased risk for smoking related cancers was mainly due to an increased risk of lung cancer (1.86 per Sv, 0.26 to 4.01). Other smoking related cancers showed little evidence of an increased risk (0.21 per Sv, < 0 to 2.01). Risk estimates for mortality from non-malignant respiratory diseases and from chronic obstructive bronchitis and emphysema were raised but not significantly different from zero (excess relative risk per Sv 1.16, −0.53 to 3.84, and 2.12, −0.57 to 7.46, respectively).


Results from our study show that an excess risk of cancer exists, albeit small, even at the low doses and dose rates typically received by nuclear workers in this study. The 15 country study allowed the compilation of the largest body of direct evidence to date concerning the effects of low dose chronic exposure to ionising radiation. Our risk estimates mainly reflect risks in men, as there were few exposed women in the cohort.

Dosimetric measurement errors

Reliable estimates of dose were systematically available only for external exposure to higher energy photons so our results are restricted to workers exposed mainly to these radiation types. A detailed study of historical practices and technology allowed us to identify and quantify the major sources of errors. Analyses were based on organ dose estimates, which we adjusted to account for the main sources of systematic errors.

All cancer excluding leukaemia

We found a significantly increased risk for all cancers (excluding leukaemia). The central risk estimate was higher than the linear extrapolation from the A bomb survivors. It is unlikely that this could be due to ascertainment bias, with physicians being more likely to list cancer as the underlying cause of death for workers with higher exposures, as the excess relative risk for all non-cancer mortality was weakly positive (0.20, −0.26 to 0.72).

We could not adjust directly for possible confounding by variables such as smoking, diet, and occupational exposures as information was not available. Some of these factors—particularly smoking16 and diet—are strongly related to socioeconomic status and adjustment for this will have partially controlled for their effects. Factors such as smoking can confound the association between radiation dose and risk only if they are related both to risk of cancer and to dose. Some cohort studies have found an association between radiation dose and smoking,17 18 while others have not.1921

Although the estimated risk for mortality from lung cancer was particularly high, mortality from smoking related cancers other than lung cancer showed little evidence of a relation with dose. Indeed, the central risk estimate for cancers unrelated to smoking was higher than that for smoking related cancers other than lung caner, indicating that confounding by smoking is unlikely to explain all of the relation found between all cancer risk and radiation dose. On the other hand, the non-significantly increased risks for mortality from non-malignant smoking related diseases indicate a possible effect of smoking. The risk estimates for mortality from all groups of cancers related and unrelated to smoking, however, are consistently two to three times higher than, but statistically compatible with, the risk estimate for solid cancers from the A bomb analyses (table 3). Taken together, these findings indicate that a confounding effect by smoking may be partly, but not entirely, responsible for the estimated increased risk for mortality from all cancers other than leukaemia.

The findings for all cancers excluding leukaemia were not greatly influenced by data from any one country: formal tests for heterogeneity provided no evidence for differences in risk between countries, cohorts, or groups of facilities (P > 0.20). Figure 2 shows the excess relative risk per Sv in the larger cohorts (> 100 cancer deaths); the risk estimate for Canada is the largest. Analyses excluding one cohort or country at a time produced excess relative risks per Sv ranging from 0.58 (excluding Canada) to 1.25 (excluding the UK), all consistently higher than, but compatible with, the estimate from A bomb analyses. Only when we excluded Canada was the excess relative risk no longer significantly different from zero (0.58, −0.22 to 1.55).

Fig 2
Fig 2

Excess relative risks per Sv for all cancer excluding leukaemia in cohorts with more than 100 deaths (NPP=nuclear power plants, ORNL=Oak Ridge National Laboratory)

Sensitivity analyses of different lag periods showed that both the risk estimates and their uncertainties increased with increasing lag. The excess relative risk per Sv ranges from 0.76 (0.07 to 1.59) with a lag of five years to 1.68 (0.22 to 3.48) with a lag of 20 years. The estimates are all statistically compatible with the linear extrapolation from the A bomb survivors.

Leukaemia excluding chronic lymphocytic leukaemia

Although our estimate of risk of leukaemia is not significantly different from zero, it is similar to estimates from previous large scale studies of nuclear workers.5 7 Furthermore, it is intermediate between estimates obtained by fitting a linear and a linear quadratic dose-response model to data on men exposed to the A bomb at age 20-60. The excess relative risk per Sv shows only a small increase with increasing lag periods, from 1.93 (< 0 to 8.47) with a lag of two years to 2.53 (< 0 to 10.45) with a lag of 10 years.

The preferred model for the A bomb data includes an effect of time since exposure.14 Patterns of risk of cancer after low dose protracted exposures are, however, not necessarily the same as those observed in A bomb studies. Indeed, the data for nuclear workers did not show evidence of a time since exposure effect (not shown).

Our results are not independent of previous combined analyses.5 7 Analyses excluding workers from these earlier cohorts, however, yielded similar conclusions.

Implications for radiation protection

The general practice in radiation protection is to estimate risks for protracted exposures to low doses by extrapolating from situations of acute exposure to high doses. For this, a linear dose response model with no threshold is assumed and risk estimates are divided by two to allow for the assumed reduced carcinogenicity of exposures received at low dose rates.2 For leukaemia, this is similar to using the linear term of a linear quadratic model. The central risk estimate for leukaemia from this study (and from previous studies of nuclear workers) would support this practice. The confidence interval is wide, however, and findings are also compatible with no reduction, as well as with greater reductions of risk at low doses.

For mortality from all cancers excluding leukaemia, the central risk estimates are two to three times higher than the linear extrapolation from the A bomb survivors. The confidence intervals are wide, however, and findings are statistically compatible with the current bases for radiation protection standards.

Current recommendations form the International Commission on Radiological Protection (ICRP) are to limit occupationaldoses to 100 mSv over five years (not to exceed 50 mSv in any one year) and doses to the public to 1 mSv per year.2 Our estimates suggest that a cumulative exposure of 100 mSv would lead to a 9.7% (1.4 to 19.7%) increased mortality from all cancers excluding leukaemia and a 5.9% (−2.9 to 17.0%) increased mortality from all cancers excluding leukaemia, lung, and pleura compared with background rates. The corresponding figure is 19% (< 0 to 84.7%) for mortality from leukaemia excluding chronic lymphocytic leukaemia. Less than 5% of workers in this study received cumulative doses of the order of 100 mSv over their entire career, however, and most of these doses were received in the early years of the nuclear industry, when protection standards were less stringent than today. Overall, on the basis of our central risk estimates, we estimate that 1-2% of deaths from cancer (including leukaemia) among workers in this cohort may be attributable to radiation.

What is already known on this topic

Current radiation protection standards are based mainly on data from the survivors of the atomic bomb in Japan

The estimation of risks after low dose protracted or fractionated exposures to ionising radiation is controversial

What this study adds

A small excess risk of cancer exists, even at the low doses typically received by nuclear industry workers in this study


We have provided radiation risk estimates from the largest study of nuclear industry workers conducted so far. These estimates are higher than, but statistically compatible with, the current bases for radiation protection standards. The confidence intervals range from values lower than those derived by linear extrapolation from data from A bomb survivors up to values that exceed this extrapolation by a factor of six for cancers other than leukaemia and nearly three for leukaemia. These results suggest that an excess risk of cancer exists, albeit small, even at the low doses and dose rates typically received by nuclear workers in this study.


We are grateful to Richard Doll, Jacques Estève, and Bruce Armstrong who helped to start this study; to the late Len Salmon who inspired the study of errors in doses; to past members of the dosimetry and epidemiology subcommittees (William Murray, Robert Rinsky) and of the international study group (the late E Gubéran, Y Hosoda, T Iwasaki, G Kendall, M Murata, T Rytomaa); to everyone in the participating countries who worked in the collection and validation of the data used in the study; and to the representatives and staff of the nuclear facilities included in the study for their open collaboration. This report uses data obtained from the Radiation Effects Research Foundation (RERF), Hiroshima and Nagasaki, Japan. RERF is a private, non-profit foundation funded by the Japanese Ministry of Health, Labour and Welfare and the US Department of Energy through the National Academy of Sciences. The conclusions in this report are those of the authors and do not necessarily reflect the scientific judgment of RERF or its funding agencies.


  • Contributors ECa designed and coordinated the international study, took part in data analysis, interpretation, and writing of the paper, and is guarantor. MV took part in data analysis, interpretation, and writing of the paper for the international study. As members of the epidemiology subcommittee MB, EG, MH, CHi, GH, JKa, CM, MS-B, and TY contributed to the conception and design, the development of the analytical strategy, and the analysis and interpretation of the data of the international study. They also contributed to the collection and validation of data in their own countries. As members of the dosimetry subcommittee FB, GC, JJF, CHa, BH, MMarshall, IT-C, and DU developed the protocol for the study of errors in doses, collected data on dosimetry practices, and participated in the review and analysis of dosimetry questionnaires and in the identification and quantification of errors in photon dose estimates. The study of errors in doses was the topic of IT-C's PhD dissertation and postdoctoral fellowship, and she was involved in all of the steps of data acquisition, validation, and analysis and in the planning and conducting of the dosimetry experiments and the derivation of the dosimetric bias conversion factors. The other members of the international study group (YOA, PA, AA, JMB, JBS, AB, PD, ADS, ME, HE, GE, LMG, GG, RH, KH, HH, AK, JKu, HM, AMa, IT, MU) took part in the design of the common protocol and were responsible for implementation of the core protocol and the collection and validation of data in their countries. FR-A, AR, MT-L, and KV coordinated data collection or otherwise contributed to data acquisition, analysis, and interpretation of data at the national level in their countries. EA, ECo, AMo, and HT were responsible for management of the international database and for data validation and analysis at IARC. MMartuzzi and DBR assisted in validation of the data at the international level, implementation of the protocol at the national level, and provided assistance to national collaborators through contacts and site visits. MSP assisted in the validation and analysis of the international dataset. All authors critically reviewed earlier drafts for important intellectual content and approved the final version of the paper.

  • Funding European Union (contracts F13P-CT930066, F14P-CT96-0062, FIGH-CT1999-20001); US Centers for Disease Control (Co-operative agreement U50/CCU011778); Canadian Nuclear Safety Commission; Japanese Institute for Radiation Epidemiology, Australian Nuclear Science and Technology Organisation; Nuclear Research Center (SCKCEN), Belgium; Health Canada and Statistics Canada; La Ligue Nationale contre le Cancer, France; La Compagnie Générale des Matière Nucléaire, France; Electricité de France; Ministry of Education, Culture, Sports, Science and Technology in Japan; Ministry of Science and Technology (MOST) in Korea; Spanish Nuclear Safety Council; US Department of Energy. These sponsors had no role in study design, data collection, analysis, or interpretation. IT-C received funding from the Association pour la Recherche contre le Cancer (ARC, France); MSP and DBR were the recipients, respectively, of an IARC postdoctoral fellowship and of an ORAU fellowship during their stay at IARC.

  • Competing interests C Hacker, B Heinmiller, H Hyvonen, M Marshall, A Rogel, J Bernar Solano, M Eklöf, and K Holan are (or have been in the past five years) employees of the nuclear industry or have links to the nuclear industry in their country. They were appointed to the international study group and or the dosimetry subcommittee as experts because of their critical knowledge and experience in historical radiation protection practices and dosimetry. None of them had influence on decisions concerning analysis of the results.

  • Ethical approval The study was approved by the IARC ethical review committee and by the relevant ethical committees of the participating countries.


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