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. 1999 May 29;318(7196):1443–1450. doi: 10.1136/bmj.318.7196.1443

Cancer in children of nuclear industry employees: report on children aged under 25 years from nuclear industry family study

Eve Roman a, Pat Doyle b, Noreen Maconochie b, Graham Davies b, Peter G Smith b, Valerie Beral c
PMCID: PMC27886  PMID: 10346768

Abstract

Objective

To determine whether children of men and women occupationally exposed to ionising radiation are at increased risk of developing leukaemia or other cancers before their 25th birthday.

Design

Cohort study of children of nuclear industry employees.

Setting

Nuclear establishments operated by the Atomic Energy Authority, Atomic Weapons Establishment, and British Nuclear Fuels.

Subjects

39 557 children of male employees and 8883 children of female employees.

Main outcome measures

Cancer incidence in offspring reported by parents. Employment and radiation monitoring data (including annual external dose) supplied by the nuclear authorities.

Results

111 cancers were reported, of which 28 were leukaemia. The estimated standardised incidence ratios for children of male and female employees who were born in 1965 or later were 98 (95% confidence interval 73 to 129) and 96 (50 to 168) for all malignancies and 109 (61 to 180) and 95 (20 to 277) for leukaemia. The leukaemia rate in children whose fathers had accumulated a preconceptual dose of ⩾100 mSv was 5.8 times that in children conceived before their fathers’ employment in the nuclear industry (95% confidence interval 1.3 to 24.8) but this was based on only three exposed cases. Two of these cases were included in the west Cumbrian (“Gardner”) case-control study. No significant trends were found between increasing dose and leukaemia.

Conclusions

Cancer in young people is rare, and our results are based on small numbers of events. Overall, the findings suggest that the incidence of cancer and leukaemia among children of nuclear industry employees is similar to that in the general population.The possibility that exposure of fathers to relatively high doses of ionising radiation before their child’s conception might be related to an increased risk of leukaemia in their offspring could not be disproved, but this result was based on only three cases, two of which have been previously reported. High conceptual doses are rare, and even if the occupational association were causal, the number of leukaemias involved would be small; in this study of over 46 000 children, fewer than three leukaemias could potentially be attributed to such an exposure.

Key messages

  • This cohort study examined cancer diagnosed before the age of 25 years in children of workers at three nuclear authorities in the United Kingdom

  • Overall the incidence of all cancers and of leukaemia was similar to that expected in the general population

  • The possibility that exposure of fathers to relatively high doses of ionising radiation before their child’s conception might in some way be related to an increased risk of leukaemia in their offspring could not be disproved, but this result was based on only three cases, two of which have been previously reported in the west Cumbrian (“Gardner”) case-control study

Introduction

The incidence of leukaemia and non-Hodgkin’s lymphoma in young people living near certain nuclear establishments in the United Kingdom has been the subject of much research. 123 Of particular concern has been the sustained increased incidence of these cancers in children and young adults living in the Cumbrian village of Seascale, near British Nuclear Fuels’ Sellafield reprocessing plant.1,6,7,18,21 In addition, increased rates of leukaemia and non-Hodgkin’s lymphoma have been reported in young people living near the Atomic Energy Authority’s Dounreay plant4 9and the Atomic Weapons Establishments at Aldermaston and Burghfield.8 13

The nuclear industry family study was set up to investigate possible links between child health and parents’ occupational exposure to ionising radiation.24 Gardner et al’s report,10 suggesting an association between leukaemia in the under 25s and paternal preconceptual exposure to external sources of ionising radiation at work, was published while our study was still at the planning stage. The interpretation of Gardner et al’s findings10,12 continues to be debated,19,2530 and this paper focuses on our findings for cancer in the under 25s.

Participants and methods

Information about the study is given elsewhere.24 Briefly, the study population comprised employees of three nuclear authorities: the Atomic Weapons Establishment, the Atomic Energy Authority, and British Nuclear Fuels. All current employees of these three authorities, and past employees of the last two under 75 years old whose details were recorded on the pensions database, were surveyed over the four years 1993 to 1996. For the purposes of the study, employers provided each subject with a unique personal identifier, which was used to link respondents’ data to industry employment and monitoring records (including annual radiation dose).

After undelivered post was excluded, the response rate was 82% for male workers and 88% for female workers, with 39 557 live births being reported by 18 131 fathers and 8883 by 4435 mothers.24 The total number of children in the study was 46 107; 2333 children had both a mother and father in the surveyed population. When a parent reported that one of their children had had a serious illness, such as cancer, more information was requested about the condition and signed consent was sought to access relevant medical notes. Parents were asked to forward consent forms to living children aged 18 years or over.

Statistical methods

Each child contributed offspring-years at risk from their date of birth until the earliest of the following events: 25th birthday, date of survey, diagnosis of cancer under consideration, or death. Date of conception was estimated as date of birth minus 266 days, except when more precise information on gestational age was available. All analyses were performed with Stata software.31 P values are two sided, with values less than 0.05 indicating significance.

External comparisons

We obtained annual cancer incidence rates specific for sex and five year age groups for England and Wales, 1971-89 from the Office for National Statistics. National cancer registration in England and Wales did not have an acceptable level of coverage until 1971,32and data for the 1990s were unavailable at the time of analysis. We therefore decided in advance to restrict the comparison with the general population to births occurring in 1965 or later, using average national rates for the five years 1971-5 to estimate rates before 1971 and average rates for the five years 1985-9 to estimate rates after 1989. For births occurring in 1965 or later, offspring-years at risk were stratified by sex, age (five year groups), and calendar period (single years), and the numbers of cancers expected on the basis of the England and Wales rates were calculated. Exact 95% confidence intervals and P values for the resulting standardised incidence ratios were based on the Poisson distribution.33

Internal cohort comparisons

We estimated the effect of parental exposure to radiation on the risk of malignancy by rate ratios (hazard ratios) using Cox proportional hazards modelling, with age as the time variable and adjusting for calendar period in 10 year intervals and child’s sex.34 In analyses of radiation exposure at any time, parental exposure wastreated as a time dependent variable. Hence, the same child could contribute offspring-years both to the “unexposed” category (offspring-years occurring before first parental exposure) and to one or more of the “exposed” categories (offspring-years occurring after first parental exposure). For analyses relating to parental exposures occurring before conception, however, all offspring-years were assigned to the same exposure group. Trends of increasing risk with cumulative preconceptual radiation dose were tested by using Cox proportional hazards modelling. Only children whose fathers had been monitored for external sources of ionising radiation before their conception were included in such analyses, the actual preconceptual dose accumulated being modelled using linear, quadratic, or higher order terms.

Because many workers had more than one child in the study, standard errors for the rate ratios were not calculated by standard methods, which assume independence between observations. Instead, we used a robust method based on the “sandwich estimate” of the standard error in all regression analyses.35,36 We then assessed the significance of the contribution of variables to the model using the Wald test with the robust variance estimate.37 38

The hypothesis that occupational preconceptual exposure of fathers to external sources of ionising radiation increases the risk of leukaemia in their offspring derives mainly from the case-control study conducted by Gardner and colleagues.10 Gardner et al studied leukaemia and non-Hodgkin’s lymphoma in those born in west Cumbria and diagnosed there before their 25th birthday between 1 January 1950 and 31 December 1985.11 Because of the potential for overlap with our study, analyses relating to paternal preconceptual exposure were conducted both with and without children born in Cumbria on, or before, 31 December 1985; this last group comprised 5950 (15%) children of male workers and 1170 (13%) of female workers.

Results

The 39 557 children of male workers and 8883 children of female workers respectively contributed 716 325 and 156 304 offspring-years at risk to the analysis. The median length of follow up (up to a maximum 25 years) was 23 years for children of male workers and 22.7 years for children of female workers (table 1). At the time of survey, the oldest child was 58 (born in 1937) and the youngest was less than a month (born in 1996). The proportion of parents monitored for exposure to ionising radiation at some time before their child’s 25th birthday was 80% for male employees compared with 25% for female employees. Likewise, although 40% of children of male employees had a father who was monitored before their conception, only 9% of children of female employees had a mother who was similarly exposed (table 1).

Table 1.

Description of children and malignancies diagnosed before the age of 25 years, reported by parents employed by nuclear authorities. Values are numbers (percentages) of children unless stated otherwise

Sex of reporting parent
Male Female
Total liveborn children 39 557 8883
Median length of follow-up (years)* 23.0 22.7
Year of birth:
 Before 1965 13 995 (35) 2829 (32)
 1965-1974 9 263 (23) 2422 (27)
 1975-1984 8 609 (22) 1480 (17)
 1985-1996 7 690 (19) 2152 (24)
Age of child at survey (years):
 <5 4 487 (11) 1297 (15)
 5-9 4 234 (11) 1009 (11)
 10-14 4 456 (11) 810 (9)
 15-19 4 034 (10) 750 (8)
 20-24 4 265 (11) 1120 (13)
 ⩾25 18 081 (46) 3897 (44)
Parental monitoring:
 Never monitored 8 034 (20) 6683 (75)
 Ever monitored 31 523 (80) 2200 (25)
 Monitored before conception 15 898 (40) 801 (9)
No of malignancies (No validated):
 All malignancies    94 (92)   22 (20)
 Bone§     8 (8)   2 (2)
 Testis     2 (2) 0
 Central nervous system§    17 (17)   7 (7)
 Hodgkin’s disease§    14 (13)   3 (3)
 Non-Hodgkin’s lymphoma§     6 (6)   2 (1)
 Leukaemia    22 (22)   6 (5)
 All other malignancies§    25 (24)   2 (2)
*

Up to the child’s 25th birthday, death, or time of survey. 

Monitoring of parent at any time up to the child’s 25th birthday, death, or time of survey (including before birth or conception). 

ICD-9 codes: all malignancies (1400-2089, 2250, 2375, 2396); bone (1700-1709); testis (1860-1869); central nervous system (1910-1929, 1943-1944, 2250, 2375, 2396); Hodgkin’s disease (2010-2019); non-Hodgkin’s lymphoma (2000-2008, 2020-2022, 2024,2026-2029, 2040-2089); leukaemia (2040-2089). 

Five children had both a father and mother in the survey. To preserve confidentiality, site specific data are shown only where there were two or more reports. 

§

Includes one child with both father and mother in the survey population. 

A total of 111 children were reported to have developed a malignancy before their 25th birthday. Five of these, none of whom had leukaemia, had both parents in the study. The earliest year of diagnosis was 1951 and the latest was 1993. Confirmatory evidence in the form of a cancer registration, death certificate, or entry in medical notes was located for 108 (97%) of the 111 children.

Comparison with the general population

Table 2 compares the numbers of cancers diagnosed in children born in 1965 or later, comprising around two thirds of the total population of children, with the numbers expected based on national rates. None of the standardised incidence ratios was significantly different from 100. For all malignancies, the observed and expected numbers among children of male and female workers were almost identical, the ratios for 0 to 24 year olds being 98 (95% confidence interval 73 to 129) and 96 (50 to 168) respectively. The incidence ratios for leukaemia were also close to 100.

Table 2.

Numbers of cancers diagnosed in children born in 1965 or later compared with number expected on basis of cancer incidence rates for England and Wales

Father reported
Mother reported
Cancer and age group (years) Observed Expected Standardised incidence ratio (95% CI)* Observed Expected Standardised incidence ratio (95% CI) *
All malignancies

0-24 52 52.87  98 (73 to 129) 12 12.47  96 (50 to 168)
0-14 36 36.50  99 (69 to 137) 9 8.30 108 (50 to 206)
Leukaemia and non-Hodgkin’s lymphoma
0-24 20 16.95 118 (72 to 182) 5 3.92 127 (41 to 298)
0-14 18 14.01 128 (76 to 203) 4 3.19 126 (34 to 321)
Leukaemia
0-24 15 13.71 109 (61 to 180) 3 3.17  95 (20 to 277)
0-14 14 11.96 117 (64 to 196) 3 2.73 110 (23 to 321)
All malignancies except leukaemia and non-Hodgkin’s lymphoma
0-24 32 35.95  89 (61 to 126 ) 7 8.55  82 (33 to 169)
0-14 18 22.50  80 (47 to 126) 5 5.12  98 (32 to 228)
*

Adjusted for sex, age (5 year groups), and calendar period (single years). 

Comparisons within the cohort

Parental employment and monitoring at any time

Table 3 gives the offspring-years at risk and cancers among children of nuclear industry workers classified according to their parents’ history of employment in the industries surveyed and monitored for radiation exposure at any time before their child’s 25th birthday. For each malignancy group the baseline for all comparisons is the cancer rate in offspring before their parent had a record of employment of monitoring. Data in the second category relate to cancer risk after parental first employment but before first monitoring, and data in the third category to cancer risk after first monitoring.

Table 3.

Cancers and offspring-years at risk in children of nuclear workers, classified according to parental history of employment and monitoring for potential exposure to ionising radiation

 Male workers
Female workers
No of cancers (offspring-years*) Rate ratio (95% CI) No of cancers (offspring-years*) Rate ratio (95% CI)
All malignancies

Before employment and monitoring§ 16 (156 218) 1.0 8 (84 165) 1.0
After employment, not monitored§ 10 (123 283) 0.6 (0.3 to 1.5) 12 (55 128) 2.7 (1.1 to 7.0)
Monitored (all)§: 68 (436 824) 1.2 (0.7 to 2.2) 2 (17 011) 1.5 (0.3 to 7.1)
 External radiation only 34 (228 334) 1.2 (0.6 to 2.2) 2 (10 942)  2.3 (0.5 to 10.6)
 External and internal 34 (208 490) 1.2 (0.7 to 2.4) 0 (6 069) 0 (–)
Leukaemia and non-Hodgkin’s lymphoma
Before employment and monitoring§  3 (156 252) 1.0 4 (84 183) 1.0
After employment, not monitored§  2 (123 346) 0.7 (0.1 to 4.5) 4 (55 163) 1.6 (0.4 to 6.1)
Monitored (all)§: 23 (437 023) 2.4 (0.6 to 9.5) 0 (17 021) 0 (–)
 External radiation only  9 (228 422) 1.8 (0.4 to 7.9) 0 (10 952) 0 (–)
 External and internal 14 (208 601)  3.0 (0.7 to 13.0) 0 (6 069) 0 (–)
Leukaemia
Before employment and monitoring§  2 (156 253) 1.0 4 (84 153) 1.0
After employment, not monitored§  2 (123 346) 1.2 (0.2 to 8.6) 2 (55 170) 1.2 (0.3 to 5.5)
Monitored (all)§: 18 (437 050)  3.2 (0.6 to 15.7) 0 (17 021) 0(–)
 External radiation only  7 (228 437) 2.4 (0.4 to13.1) 0 (10 952) 0 (–)
 External and internal 11 (208 613)  4.1 (0.8 to 21.8) 0 (6 069) 0 (–)
All malignancies except leukaemia and non-Hodgkin’s lymphoma
Before employment and monitoring§ 13 (156 230) 1.0 4 (84 177) 1.0
After employment, not monitored§  8 (123 300) 0.6 (0.2 to 1.6) 8 (55 159)  3.9 (1.0 to 14.4)
Monitored (all)§: 45 (436 968) 1.0 (0.5 to 1.8) 2 (17 011)  3.2 (0.6 to 17.8)
 External radiation only 25 (228 360) 1.0 (0.5 to 2.1) 2 (10 942)  4.8 (0.9 to 26.4)
 External and internal 20 (208 608) 0.9 (0.4 to 1.8) 0 (6 069) 0 (–)
*

Offspring-years up to diagnosis, death, or date of survey. 

Estimated rate ratios adjusted for calendar period, age and sex of child, and for the number of children born to each parent. 

According to date of first service with nuclear authority in personnel record supplied by employer. 

§

Monitoring defined as presence of a record of monitoring for external sources of ionising radiation at Atomic Weapons Establishments, Atomic Energy Authority, British Nuclear Fuels or a previous employer, or date first externally monitored present in personnel record, or flag/date of monitoring for internal radionuclides. 

Relatively few children had mothers who were monitored for external sources of ionising radiation (table 3). Indeed, the rarity of this occupational exposure in women, coupled with the rarity of cancer in the under 25s resulted in small numbers of cases in most exposure categories. For example, no leukaemias were reported in children of women who were monitored for exposure to external sources of ionising radiation. Because of lack of data, no further analyses of cancer in children of female employees are presented here.

Among children of male workers, there were no significant variations in cancer risk with paternal history of employment in the nuclear industry or with paternal monitoring for radiation exposure (table 3). Furthermore, there was no evidence that the pattern of rate ratios varied with employer, date of first employment, or whether the respondent was a current or past worker at the time of the survey (data not shown).

Paternal employment before conception

Table 4 gives the findings relating to paternal employment, monitoring status, and estimated dose of ionising radiation in the preconceptual period. The preconceptual dose groupings are similar to those used by Gardner and colleagues,10,12 except that children of fathers with a record of monitoring for exposure to ionising radiation for whom there was no recorded dose are included in the lowest dose group (in our data none of the fathers of children with malignancies had recorded doses below 0.1 mSv).

Table 4.

Cancers under age of 25 years in children of male nuclear workers, classified according to paternal employment history before conception, monitoring for radiation exposure, and estimated radiation dose with separate analysis excluding children who may have been included in the study by Gardner et al10

All children
Excluding children born in Cumbria before 1986
No of cancers (offspring-years*) Rate ratio (95% CI) No of cancers (offspring-years*) Rate ratio (95% CI)
All malignancies
Before employment and monitoring§ 39 (379 025) 1.0 31 (325 479) 1.0
After employment, not monitored§ 16 (95 115) 1.5 (0.8 to 2.7) 14 (90 478) 1.5 (0.8 to 2.8)
Monitored (all)§: 39 (242 186) 1.4 (0.9 to 2.2) 29 (182 763) 1.5 (0.9 to 2.5)
 External radiation only 23 (150 648) 1.4 (0.8 to 2.3) 18 (120 539) 1.4 (0.8 to 2.6)
 External and internal 16 (91 538) 1.5 (0.8 to 2.7) 11 (62 224) 1.6 (0.8 to 3.2)
Cumulative external dose (mSv):
 <50 29 (187 197) 1.4 (0.8 to 2.2) 23 (154 736) 1.4 (0.8 to 2.4)
 50- 4 (26 660) 1.3 (0.5 to 3.8) 2 (14 880) 1.2 (0.3 to 5.4)
 ⩾100 6 (23 431) 2.2 (0.9 to 5.3) 4 (8 570)  4.1 (1.4 to 11.8)
Estimated cumulative dose in 6 months before conception (mSv):
 <5 31 (199 180) 1.3 (0.8 to 2.2) 25 (163 313) 1.4 (0.8 to 2.5)
 5- 3 (20 026) 1.4 (0.4 to 4.5) 1 (9 144) 1.1 (0.1 to 8.1)
 ⩾10 5 (17 986) 2.5 (1.0 to 6.5) 3 (5 648)  5.1 (1.6 to 16.9)
Leukaemia and non-Hodgkin’s lymphoma
Before employment and monitoring§ 11 (379 173) 1.0  7 (325 594) 1.0
After employment, not monitored§ 3 (95 170) 1.0 (0.3 to 3.6) 3 (90 527) 1.4 (0.3 to 5.5)
Monitored (all)§ 14 (242 279) 1.8 (0.7 to 4.4) 10 (182 841) 2.2 (0.7 to 6.6)
 External radiation only  7 (150 705) 1.5 (0.5 to 4.2)  6 (120 582) 2.0 (0.6 to 7.0)
 External and internal 7 (91 574) 2.3 (0.8 to 6.6) 4 (62 259) 2.4 (0.6 to 9.4)
Cumulative external dose (mSv):
 <50 10 (187 255) 1.7 (0.6 to 4.3)  9 (154 782) 2.3 (0.8 to 7.2)
 50- 1 (26 681) 1.2 (0.2 to 9.4) 0 (14 898) 0.0 (-)
 ⩾100 3 (23 445)  3.9 (1.0 to 15.7) 1 (8 584)  4.3 (0.5 to 40.5)
Estimated cumulative dose in 6 months before conception (mSv):
 <5 11 (199 255) 1.7 (0.7 to 4.3)  9 (613 378) 2.2 (0.7 to 6.8)
 5- 0 (20 030) 0.0 (-) 0 (9 145) 0.0 (-)
 ⩾10 3 (18 000)  5.4 (1.4 to 20.5) 1 (5 661)  7.4 (0.8 to 66.5)
Leukaemia
Before employment and monitoring§  8 (379 188) 1.0  5 (325 607) 1.0
After employment, not monitored§ 2 (95 181) 1.0 (0.2 to 4.4) 2 (90 538) 1.3 (0.3 to 6.9)
Monitored (all)§: 12 (242 280) 2.2 (0.8 to 6.1)  9 (182 842)  2.9 (0.8 to 10.3)
 External radiation only  7 (150 705) 2.1 (0.7 to 6.5)  6 (120 582)  3.0 (0.8 to 11.5)
 External and internal 5 (91 575) 2.4 (0.7 to 8.3) 3 (62 260)  2.7 (0.6 to 13.5)
Cumulative external dose (mSv):
 <50  8 (187 256) 1.9 (0.7 to 5.7)  8 (154 783)  3.1 (0.8 to 11.1)
 50- 1 (26 681)  1.7 (0.2 to 14.2) 0 (14 898) 0.0 ( to )
 ⩾100 3 (23 445)  5.8 (1.3 to 24.8) 1 (8 584)  6.6 (0.7 to 67.1)
Estimated cumulative dose in 6 months before conception (mSv):
 <5  9 (199 257) 2.0 (0.7 to 5.9)  8 (163 379)  2.9 (0.8 to 10.5)
 5- 0 (20 030) 0.0 (-) 0 (9 145) 0.0 (-)
 ⩾10 3 (18 000)  7.7 (1.9 to 31.0) 1 (5 661)  11.0 (1.2 to 105.0)
All malignancies except leukaemia and non-Hodgkin’s lymphoma
Before employment and monitoring§ 28 (379 093) 1.0 24 (325 543) 1.0
After employment, not monitored§ 13 (95 131) 1.7 (0.9 to 3.3) 11 (90 494) 1.5 (0.7 to 3.1)
Monitored (all)§: 25 (242 274) 1.3 (0.7 to 2.2) 19 (182 834) 1.3 (0.7 to 2.3)
 External radiation only 16 (150 684) 1.3 (0.7 to 2.4) 12 (120 574) 1.2 (0.6 to 2.5)
 External and internal 9 (91 590) 1.2 (0.6 to 2.5) 7 (64 260) 1.3 (0.6 to 3.1)
Cumulative external dose (mSv):
 <50 19 (187 264) 1.2 (0.7 to 2.2) 14 (154 803) 1.1 (0.6 to 2.1)
 50- 3 (26 674) 1.4 (0.4 to 4.7) 2 (14 880) 1.6 (0.4 to 7.2)
 ⩾100 3 (23 438) 1.5 (0.5 to 5.0) 3 (8 573)  4.0 (1.2 to 13.6)
Estimated cumulative dose in 6 months before conception (mSv):
 <5 20 (199 261) 1.2 (0.7 to 2.1) 16 (163 380) 1.2 (0.6 to 2.2)
 5- 3 (20 026) 1.9 (0.6 to 6.3) 1 (9 145)  1.4 (0.2 to 10.7)
 ⩾10 2 (17 993) 1.4 (0.3 to 5.9) 2 (5 652)  4.4 (1.1 to 18.5)
*

Offspring-years up to diagnosis, death, or date of survey. 

Estimated rate ratios adjusted for calendar period, age and sex of child, and for the number of children born to each parent. 

According to date of first service with nuclear authority in personnel record supplied by employer. 

§

Monitoring defined as presence of a record of monitoring for external sources of ionising radiation at Atomic Weapons Establishment, Atomic Energy Authority, British Nuclear Fuels or a previous employer, or date first externally monitored present in personnel record, or flag/date of monitoring for internal radionuclides. 

Cumulative paternal dose. For 947 (3%) of children (3265 offspring-years) the cumulative dose at conception was not known, either because, although there was evidence that the father had been internally monitored, there was no external dose record or because the first external dose record was a transfer dose, or because there was evidence from the personnel record that the father had been monitored but there was no external dose record. 

Table 4 includes more cancers and offspring-years in the baseline category (and correspondingly fewer in the employed and monitored categories) than table 3 becausepaternal monitoring and employment is considered only to the point of the child’s estimated date of conception. For leukaemia, the estimated rate ratio in children whose fathers had a record of monitoring for radiation exposure before their conception was 2.2 (0.8 to 6.1; based on 12 exposed cases). Among children whose fathers were monitored for external sources alone it was 2.1 (0.7 to 6.5) and among children whose fathers were also monitored for radionuclides it was 2.4 (0.7 to 8.3). With respect to recorded whole body dose, the rate ratio for leukaemia in those whose fathers had accumulated a lifetime dose of ⩾100 mSv before their child’s conception was 5.8 (1.3 to 24.7). This excess was based on three exposed cases, and the fathers of these three children also had estimated doses in the six months before conception of 10 mSv or more (rate ratio 7.7; 1.9 to 31.0). However, among those who had been monitored for external radiation exposure before their child’s conception, there was no significant dose-response relation (P values for linear and quadratic terms being 0.18 and 0.16 for lifetime exposure and 0.24 and 0.28 for the six months before conception).

The rate ratios for leukaemia calculated after children born in Cumbria before 1986 (potential “Gardner” cases) were excluded are based on even smaller numbers, particularly in the high dose categories (table 4). The numbers of offspring-years at risk, however, are still substantial and the results for leukaemia are similar to those calculated for the total data. Nevertheless, it is important to note that the rate ratio estimates of 6.6 (0.7 to 67.1) for a total cumulative preconceptual dose ⩾100 mSv and 11.0 (1.2 to 105.0) for a cumulative dose ⩾10 mSv in the six months before conception were based on only one case.

The raised rate ratios for all malignancies and for leukaemia and non-Hodgkin’s lymphoma combined among all children whose fathers accrued a dose of ⩾100 mSv before their conception (and ⩾10 mSv in the six months before conception) were mainly due to leukaemia. The effect of leukaemia was less when Cumbrian births were excluded, the rate ratios for malignancies other than leukaemia and non-Hodgkin’s lymphoma being 4.0 (1.2 to 13.6, based on three exposed cases) for a lifetime paternal preconceptual dose ⩾100 mSv and 4.4 (1.1 to 18.6, two exposed cases) for a dose ⩾10 mSv in the six months before conception.

So that our results could be compared directly with the record linkage study,22,23 the analyses were repeated for the first 15 years of life. These results, which are broadly similar to those for 0-24 year olds, are available on the BMJ’s website.

Discussion

The Nuclear Industry Family Study differs in concept and design from other studies that have examined the relation between parental employment in the nuclear industry and child health. It is a within industry investigation, being more analogous to the cohort studies that examined the health of nuclear workers3944 than to the population based case-control studies that have reported on cancer in young people living in areas around nuclear sites.10,14,16,45,46 The study was resticted to employees of nuclear establishments operated by the Atomic Energy Authority, Atomic Weapons Establishment, and British Nuclear Fuels because each of these industries had at least one plant that had been subject to a report alleging an increased incidence of leukaemia in young people residing in its vicinity.1,4,6,9,10 14

In common with all studies of cancer in offspring of nuclear workers, our findings are based on small numbers of cancers. Although in the case-control studies the small numbers are principally due to the comparative rarity of employment in the nuclear industry,10,14,16,22,45,46 even in areas close to the plants, in our study they largely reflect the rarity of cancer in young people. Of the 46 107 children included, only 111 were reported to have had cancer diagnosed before their 25th birthday and only 28 had leukaemia.

Are children of nuclear industry employees at increased risk of developing cancer?

Our study, because of its cohort design, has the potential to answer this question directly. Among children born in 1965 or later (two thirds of all children in the study) no unusual cancer patterns were evident. The incidence ratios for children of male employees were 98 (95% confidence interval 73 to 129) for all cancers and 109 (61 to 180) for leukaemia. The findings for children of female employees were similar, although based on fewer cases. Furthermore, internal analysis by parental monitoring and employment also found no firm evidence to suggest that the overall incidence differed greatly from one exposure group to another. We approached employees directly and asked them about the health of their children. Although the response rates were uniformly high and all haematological malignancies reported by fathers were independently corroborated, we cannot be sure that all children and malignancies were notified at survey. However, the fact that the estimated level of cancer in offspring was close to the expected value suggests that there was no overall systematic response bias within the study.

Comparison with results from west Cumbrian study

Since the publication of Gardner et al’s findings,10 discussion about the possible adverse effects of paternal exposure in the nuclear industry has revolved around leukaemia and paternal preconceptual dose of ionising radiation. The authors reported that the highest risk of leukaemia was in children whose fathers had the highest accumulated doses of ionising radiation doses before their conception (both total exposure and in the six months before conception).10,12 Compared with children of fathers with no record of monitoring for external sources of ionising radiation at Sellafield, children whose fathers had a lifetime cumulative dose ⩾100 mSv before their conception were estimated to be 8.4 (95% confidence interval 1.4 to 52.0) times more likely to develop leukaemia.12 The four cases whose fathers had a cumulative preconceptual dose ⩾100 mSv received an estimated 10 mSv or more of this dose in the six months before their child’s conception, yielding an odds ratio of 6.8 (1.5 to 31.9).12 We found rate ratios of 5.8 (1.3 to 24.7) and 7.7 (1.9 to 31.0) for these two dose categories, which is not inconsistent with Gardner et al’s results. Furthermore, in both our study and Gardner et al’s study, the same cases appeared in both the highest lifetime preconceptual dose group and the highest six months preconceptual dose category. Neither study found any significant trends of increasing risk with increasing dose when analyses were confined to those who had been monitored for radiation exposure before their child’s conception.

The population studied by Gardner et al overlaps with ours, and the similarity between the findings must be interpreted with this in mind. We attempted to overcome this problem by conducting some analyses excluding children born in Cumbria before 1986, thereby excluding all children with the potential to have been in the west Cumbrian study. Monitored Sellafield workers had been exposed to higher doses of external ionising radiation, on average, than other workers in the study. Exclusion of children born in Cumbria before 1986 therefore removed proportionally more children from the high dose group than from the low dose group. For example, although all eight cases of leukaemia remained in the <50 mSv paternal preconceptual dose category, only one remained in the ⩾100 mSv dose category (table 4). For leukaemia, the risk estimates for the high dose categories were similar to those obtained for the total data. These estimates were based, however, on a single case in the highest exposure categories. Furthermore, exclusion of Cumbrian births increased the risk estimates for malignancies other than leukaemia and non-Hodgkin’s lymphoma in the higher exposure categories.

Comparison with other studies of preconceptual exposure

Tables 5 and 6 compare our results with those of four other case-control studies 14,16,22,45 that considered paternal preconceptual radiation exposure and with those of Gardner et al.10,12 As with the west Cumbrian investigation, the studies in Caithness, west Berkshire, and Ontario looked only at cases of leukaemia and non-Hodgkin’s lymphoma diagnosed in the vicinity of nuclear plants. The record-linkage study aimed at national coverage, using birth certificate identifiers to link UK registration data on all childhood cancers to data on workers included in the National Registry for Radiation Workers.22,23

Table 5.

Summary of studies that have examined cancer risk of cancer in children whose fathers were monitored for occupational exposure to ionising radiation before their conception.* Values are risk ratios (95% confidence intervals) unless stated otherwise

West Cumbria12 Caithness14 West Berkshire16 Ontario45 Record linkage study22
Present study
All data Without west Cumbria All data Without Cumbria
Study description
Design Case-control Case-control Case-control Case-control Case-control Cohort
Age range(years) 0–24 0–24 0–4 0–14 0–14 0–24
Years of diagnosis 1950–85 1970–86 1972–89 1950–88 1952–1986 1 1951–1993
All malignancies
Monitored No data No data No data No data 1.3 (0.9 to 1.9) 1.3 (0.9 to 1.9) 1.4 (0.9 to 2.2) 1.5 (0.9 to 2.5)
⩾ 100 mSv No data No data No data No data 1.2 (0.3 to 4.3) 0.7 (0.1 to 3.4) 2.2 (0.9 to 5.3)  4.1 (1.4 to 11.8)
Leukaemia and non-Hodgkin’s lymphoma
Monitored 1.1 (0.5 to 2.7) Not reported 9.0 (1.0 to 108.8) No data 1.8 (1.1 to 3.0) 1.8 (1.1 to 3.0) 1.8 (0.7 to 4.4) 2.2 (0.7 to 6.6)
⩾100 mSv  8.6 (1.4 to 52.2) 0.0 No data No data 1.4 (0.3 to 7.2) 0.5 (0.0 to 5.2)  3.9 (1.0 to 15.7)  4.3 (0.5 to 40.5)
Leukaemia
Monitored 1.4 (0.5 to 3.9) Not reported Not reported 1.0 (0.5 to 2.2) Not reported Not reported 2.2 (0.8 to 6.1)  2.9 (0.8 to 10.3)
⩾ 100 mSv  8.4 (1.4 to 52.0) Not reported No data 0.0 Not reported Not reported  5.8 (1.3 to 24.8)  6.6 (0.7 to 67.1)
All malignancies except leukaemia and non-Hodgkin’s lymphoma
Monitored No data No data No data No data 0.9 (0.6 to 1.6) 1.3 (0.7 to 2.2) 1.3 (0.7 to 2.3)
⩾ 100 mSv No data No data No data No data  1.0 (0.1 to 13.8) 1.5 (0.5 to 5.0)  4.0 (1.2 to 13.6)
*

Further details of these studies are shown in table 6. Results from Kinlen et al’s study20 are not shown since their data were included in the record-linkage study.22 23 Findings from the case-control study conducted near the La Hague plant are also not shown since no estimates of risk were reported for monitored workers and there were no reports of workers with doses of 100 mSv or more.46 

Table 6.

 Further details of studies examining cancer risk in children whose fathers were monitored for occupational exposure to ionising radiation

Reference Cancer type No of cases
No of controls
Monitored ⩾100mSv Total Monitored ⩾100 mSv Total
Gardner et al10 (1990, 1992) Leukaemia and non-Hodgkin’s lymphoma 10 4 66 58 3 389
Leukaemia  8 4 46 40 3 276
Urquhart et al14 (1991) Leukaemia and non-Hodgkin’s lymphoma Not reported 0 12 Not reported 1  45
Roman et al16 (1993) Leukaemia and non-Hodgkin’s lymphoma  3 0 54  2 0 324
McLaughlin et al (1993)45 Leukaemia 10 0 112 81 5 894
Draper et al22 total (total minus west Cumbrian cases) All malignancies 82 (73) 6 (3 ) 34 538 (34 510) 79 (73) 7 (6) 36 912 (36 884)
Leukaemia and non-Hodgkin’s lymphoma 49 (40) 4 (1) 13 649 (13 621) 44 ( 38) 5 (4) 16 023 (15 995)
All other malignancies* 33 (33) 2 (2) 20 889 (20 889) 35 (35) 2 (2) 20 889 (20 889)
Present study total (total minus west Cumbrian cases) All malignancies 39 (29) 6 (4) 94 (74)
Leukaemia and non-Hodgkin’s lymphoma 14 (10) 3 (1) 28 (20)
Leukaemia 12 (9) 3 (1) 22 (17)
All other malignancies* 25 (19) 3 (3) 66 (4)
*

Excluding leukaemia and and non-Hodgkin’s lymphoma. 

Our study has the potential for overlap with all but the Canadian study. For Caithness and west Berkshire, the potential for overlap is small for children whose fathers were monitored before their conception and negligible for those whose fathers had doses of 100 mSv or more. We removed cases from west Cumbria to avoid overlap with Gardner et al’s study, as did the record linkage study. Case overlap between our study and the record linkage study is harder to overcome because both are national investigations. At first sight the fact that both studies estimated an 80% increase in the risk of leukaemia and non-Hodgkin’s lymphoma among children of monitored workers might be attributed to overlapping data, as around half the fathers in the record linkage study were employed at some time by the industries studied here.22 However, in the record linkage study the significantly raised risk of 1.8 (1.1 to 3.0) for leukaemia and non-Hodgkin’s lymphoma had its origins in an estimated eightfold increase in risk (95% confidence interval 1.2 to ∞) among children with fathers whose estimated doses were below 0.1 mSv.22,23 The removal of potential Gardner cases had no effect on this estimate. This observation, coupled with the knowledge that such low doses were rare in the industries studied here,24 suggests that the excess risk in the record linkage study has its origins elsewhere. The reasons for the disagreement between the studies with data on children whose fathers were exposed to ⩾100 mSv before their conception are unclear.

Conclusions

The overall incidence of cancer and leukaemia among children of nuclear workers was similar to that in the general population. The estimated risk of leukaemia in children whose fathers were monitored for exposure to radiation at work before their child’s conception was about twice that of children conceived before their fathers joined the workforces under study. Though this excess was not significant overall, significant findings were apparent for the small group of children whose fathers were exposed to relatively high doses of radiation before their conception.

Although our study is comprehensive, cancer in young people is rare and our findings are based on small numbers of cases. Our data are too few to break down into non-overlapping exposure periods; fathers exposed to high doses of external ionising radiation immediately before conception were also more likely to be exposed to high doses before that time. Similarly, fathers exposed before their child was conceived were often exposed throughout their child’s life. As well as being unable to identify relevant “time windows” of exposure, the nature of the hazardous exposure, if it exists, remains unknown. Furthermore, high preconceptual doses are rare. If there is an occupational effect associated with paternal exposure to relatively high doses of radiation, the number of leukaemias that could be attributed to such an exposure in our study is small—such exposure could account for at most three of the 22 leukaemias diagnosed in almost 40 000 reported children born during the 60 years 1937-96.

Supplementary Material

[extra: further table]

Acknowledgments

We thank the many people who contributed to the study, including management and workforce representatives who gave permission for the study to be conducted, industry staff who worked with us and, most importantly, the study participants themselves. We also thank Pat Ansell, Aurora Berra, Beverley Cooper, Patricia Fraser, Juliet Jain, Angela MacCarthy, Tuyet Ngyen, Margo Pelerin, Patrick Sampson, and Amanda Thomas. For supplying employment and dosimetry data, we thank Will Atkinson, Dallas Law and Keith Bromley (Atomic Energy Authority), George Sallit and Pauline Johnson (Atomic Weapons Establishments), and Keith Binks, Sheila Jones, and Les Scott (British Nuclear Fuels). Finally, we thank the scientific steering group (Eva Alberman, Tim Bishop, Martin Bobrow, and Dudley Goodhead) for continued support and guidance.

Papers p 1453

Footnotes

Funding: Department of Health and Health and Safety Executive. .

Competing interests: PS has received funding from British Nuclear Fuels for research on the health of Sellafield workers.

website extra: One further table is available on the BMJ’s website www.bmj.com

References

  • 1.Black D. Report of the Independent Advisory Group. Investigation of the possible increased incidence of cancer in West Cumbria. London: HMSO; 1984. [Google Scholar]
  • 2.Urquhart J, Palmer M, Cutler J. Cancer in Cumbria: the Windscale connection. Lancet. 1984;i:217–218. doi: 10.1016/s0140-6736(84)92132-9. [DOI] [PubMed] [Google Scholar]
  • 3.Gardner MJ, Winter PD. Mortality in Cumberland during 1959-78 with reference to cancer in young people around Windscale. Lancet. 1984;i:216–217. doi: 10.1016/s0140-6736(84)92131-7. [DOI] [PubMed] [Google Scholar]
  • 4.Heasman MA, Kemp IW, Urquhart JD, Black R. Childhood leukaemia in northern Scotland. Lancet. 1986;i:266. doi: 10.1016/s0140-6736(86)90794-4. [DOI] [PubMed] [Google Scholar]
  • 5.Committee on Medical Aspects of Radiation in the Environment. First report. The implications of the new data on the releases from Sellafield in the 1950s for the conclusions of the report on the investigations of the possible increased incidence of cancer in west Cumbria. London: HMSO; 1986. [Google Scholar]
  • 6.Gardner MJ, Hall AJ, Downes S, Terrell JD. Follow up study of children born elsewhere but attending schools in Seascale, west Cumbria (schools cohort) BMJ. 1987;295:819–822. doi: 10.1136/bmj.295.6602.819. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7.Gardner MJ, Hall AJ, Downes S, Terrell JD. Follow up study of children born to mothers resident in Seascale, west Cumbria (birth cohort) BMJ. 1987;295:822–827. doi: 10.1136/bmj.295.6602.822. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 8.Roman E, Beral V, Carpenter L, Watson A, Barton C, Ryder H, et al. Childhood leukaemia in the West Berkshire and Basingstoke and North Hampshire District Health Authorities in relation to nuclear establishments in the vicinity. BMJ. 1987;294:597–602. doi: 10.1136/bmj.294.6572.597. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 9.Committee on Medical Aspects of Radiation in the Environment. Second report. Investigation of the possible increased incidence of leukaemia in young people near the Dounreay nuclear establishment, Caithness, Scotland. London: HMSO; 1988. [Google Scholar]
  • 10.Gardner MJ, Snee MP, Hall AJ, Powell CA, Downes S, Terrell JD. Results of case-control study of leukaemia and lymphoma among young people near Sellafield nuclear plant in west Cumbria. BMJ. 1990;300:423–429. doi: 10.1136/bmj.300.6722.423. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 11.Gardner MJ, Hall AJ, Snee MP, Downes S, Powell CA, Terrell JD. Methods and basic data of case-control study of leukaemia and lymphoma among young people near Sellafield nuclear plant in west Cumbria. BMJ. 1990;300:429–434. doi: 10.1136/bmj.300.6722.429. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 12.Gardner MJ. Paternal occupations of children with leukaemia. BMJ. 1992;305:715. doi: 10.1136/bmj.305.6855.715. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 13.Committee on Medical Aspects of Radiation in the Environment. Third report. Report on the incidence of childhood cancer in the west Berkshire and north Hampshire area, in which are situated the Atomic Research Establishment, Aldermaston and the Royal Ordnance Factory, Burghfield. London: HMSO; 1989. [Google Scholar]
  • 14.Urquhart JD, Black RJ, Muirhead MJ, Sharp L, Maxwell M, Eden OB, et al. Case-control study of leukaemia and non-Hodgkin’s lymphoma in children in Caithness near the Dounreay nuclear installation. BMJ. 1991;302:687–692. doi: 10.1136/bmj.302.6778.687. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 15.Health and Safety Executive. Investigation of leukaemia and other cancers in the children of male workers at Sellafield. London: HMSO; 1993. [Google Scholar]
  • 16.Roman E, Watson A, Beral V, Buckle S, Bull D, Baker K, et al. Case-control study of leukaemia and non-Hodgkin’s lymphoma among children aged 0-4 years living in west Berkshire and north Hampshire health districts. BMJ. 1993;306:615–621. doi: 10.1136/bmj.306.6878.615. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 17.Parker L, Craft AW, Smith J, Dickinson H, Wakeford R, Binks K, et al. Geographical distribution of preconceptual radiation doses to fathers employed at the Sellafield nuclear installation, West Cumbria. BMJ. 1993;307:966–971. doi: 10.1136/bmj.307.6910.966. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 18.Draper GJ, Stiller CA, Cartwright RA, Craft AW, Vincent TJ. Cancer in Cumbria and in the vicinity of the Sellafield nuclear installation, 1963-90. BMJ. 1993;306:89–94. doi: 10.1136/bmj.306.6870.89. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Kinlen LJ. Can paternal preconceptional radiation account for the increase of leukaemia and non-Hodgkin’s lymphoma in Seascale? BMJ. 1993;306:1718–1721. doi: 10.1136/bmj.306.6894.1718. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 20.Kinlen LJ, Clarke L, Balkwell A. Paternal preconceptional radiation exposure in the nuclear industry and leukaemia and non-Hodgkin’s lymphoma in young people in Scotland. BMJ. 1993;306:1153–1158. doi: 10.1136/bmj.306.6886.1153. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21.Committee on Medical Aspects of Radiation in the Environment. Fourth report. The incidence of cancer and leukaemia in young people in the vicinity of the Sellafield site, west Cumbria: further studies and an update of the situation since the publication of the Black Advisory Group in 1984. London: Department of Health; 1996. [Google Scholar]
  • 22.Draper GJ, Little MP, Sorahan T, Kinlen LJ, Bunch KJ, Conquest AJ, et al. Cancer in the offspring of radiation workers—a record linkage study. Chilton: National Radiological Protection Board; 1997. (NRPB-R298.) [PMC free article] [PubMed] [Google Scholar]
  • 23.Draper GJ, Little MP, Sorahan T, Kinlen LJ, Bunch KJ, Conquest AJ, et al. Cancer in the offspring of radiation workers: a record linkage study. BMJ. 1997;315:1181–1188. [PMC free article] [PubMed] [Google Scholar]
  • 24.Maconochie N, Doyle P, Roman E, Davies G, Smith P, Beral V. The nuclear industry family study: linkage of occupational exposures to reproduction and child health. BMJ. 1999;318:53–54. doi: 10.1136/bmj.318.7196.1453. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 25.Evans HJ. Gardner report. Leukaemia and radiation. Nature. 1990;345:16–17. doi: 10.1038/345016a0. [DOI] [PubMed] [Google Scholar]
  • 26.Greaves MF. The Sellafield childhood leukemia cluster: are germ line mutations responsible? Leukemia. 1990;4:391–396. [PubMed] [Google Scholar]
  • 27.Beral V, Roman E, Bobrow M, editors. Childhood cancer and nuclear installations. London: BMJ Publishing; 1993. [Google Scholar]
  • 28.Doll R, Evans HJ, Darby SC. Paternal exposure not to blame. Nature. 1994;367:678–680. doi: 10.1038/367678a0. [DOI] [PubMed] [Google Scholar]
  • 29.Inskip H. Reay and Hope versus British Nuclear Fuels plc: issues faced when a research project formed the basis of litigation. J R Statistical Soc [Am] 1996;159:41–47. [Google Scholar]
  • 30.Wakeford R. Epidemiology and litigation—the Sellafield childhood leukaemia cases. J R Statistical Soc [Am] 1998;161:313–325. [Google Scholar]
  • 31.StataCorp. Stata statistical software; release 5.0. Texas: Stata Corporation; 1996. [Google Scholar]
  • 32.Office of Population Censuses and Surveys. Cancer statistics registrations. London: HMSO; 1987. (Series MB1 No 20.) [Google Scholar]
  • 33.Bailar JC, Ederer F. Significance factors for the ratio of a Poisson variable to its expectation. Biometrics. 1964;20:639–643. [Google Scholar]
  • 34.Breslow NE, Day NE. Statistical methods in cancer research. II. The analysis of cohort studies. Lyons: International Agency for Research on Cancer; 1980. [Google Scholar]
  • 35.Huber PJ. Proceedings of the fifth Berkeley symposium on mathematical statistics and probability. Berkley, CA: University of California Press; 1967. The behaviour of maximum likelihood estimates under non-standard conditions; p. 1. :221-33. [Google Scholar]
  • 36.Rogers WH. Sg17: Regression standard errors in clustered samples. Stata Technical Bulletin. 1993;13:19–23. [Google Scholar]
  • 37.Skinner CJ. Introduction to part A. In: Skinner CJ, Holt D, Smith TMF, editors. . Analysis of complex surveys. New York: John Wiley; 1989. [Google Scholar]
  • 38.Korn EL, Graubard BI. Simultaneous testing of regression coefficients with complex data: use of Bonferoni t statistics. American Statistician. 1990;44:270–276. [Google Scholar]
  • 39.Beral V, Inskip H, Fraser P, Booth M, Coleman D, Rose G. Mortality of employees of the United Kingdom Atomic Energy Authority, 1946-1979. BMJ. 1985;291:440–447. doi: 10.1136/bmj.291.6493.440. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 40.Smith PG, Douglas AJ. Mortality of workers at the Sellafield plant of British Nuclear Fuels. BMJ. 1986;293:845–854. doi: 10.1136/bmj.293.6551.845. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 41.Beral V, Fraser P, Carpenter L, Booth M, Brown A, Rose G. Mortality of employees of the Atomic Weapons Establishment 1951-1982. BMJ. 1988;297:757–770. doi: 10.1136/bmj.297.6651.757. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 42.Kendall G, Muirhead C, MacGibbon B, O’Hagan J, Conquest J, Goodill A, et al. First analysis of the national registry for radiation workers: occupational exposure to ionising radiation and mortality. Chilton: National Radiological Protection Board; 1992. (NRPB-R251.) [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 43.Douglas AJ, Omar RZ, Smith PG. Cancer mortality and morbidity among workers of the Sellafield plant of British Nuclear Fuels. Br J Cancer. 1994;70:1232–1243. doi: 10.1038/bjc.1994.479. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 44.Carpenter L, Higgins C, Douglas A, Fraser P, Beral V, Smith P. Combined analysis of mortality in three United Kingdom nuclear industry workforces, 1946-1988. Radiation Res. 1994;138:224–238. [PubMed] [Google Scholar]
  • 45.McLaughlin JR, Anderson TW, Clarke EA, King W. Occupational exposure of fathers to ionizing radiation and the risk of leukaemia in offspring—a case-control study. Ottowa: Atomic Energy Control Board; 1992. (AECB project No 7.157.1.) [Google Scholar]
  • 46.Pobel D, Viel JF. Case-control study of leukaemia among young people near La Hague nuclear reprocessing plant: the environmental hypothesis revisited. BMJ. 1997;314:101–106. doi: 10.1136/bmj.314.7074.101. [DOI] [PMC free article] [PubMed] [Google Scholar]

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