Abstract
Introduction
Retinoblastoma, hepatoblastoma, germ cell tumors, bone tumors, and soft tissue tumors are rare types of childhood cancer. Identifying modifiable risk factors is essential to inform primary prevention. This review aimed to systematically examine literature and synthesize risk factors for childhood rare cancers.
Methods
PubMed, Web of Science, and Embase databases were searched using lists of keywords and MeSH terms related to parental and childhood exposures. Studies were included if they were case–control or cohort studies of children under the age of 20 years at diagnosis and reported relative risks (RRs) with 95% confidence intervals (95% CIs). Pooled effect sizes (ES) and CIs for risk factors were estimated using random-effects models.
Results
A total of 75 eligible articles from Asia, Europe, Latin America, North America, and Oceania reported cases of rare childhood cancers diagnosed between 1953 and 2021. Birth weight <2,500 g was associated with hepatoblastoma (ES 3.33, 95% CI 1.30–8.54) with considerable heterogeneity across studies. A borderline association was observed for retinoblastoma (ES 1.27, 95% CI 0.99–1.63), while the estimate for germ cell tumors was elevated, albeit with a wide CI (ES 1.20, 95% CI 0.80–1.80). No association was observed for bone tumors or soft tissue tumors. Small for gestation age was associated with hepatoblastoma (ES 1.76, 95% CI 1.28–2.43). Birth weight >4,000 g was not associated with any of the studied cancer types. Assisted reproductive technology (ES 2.82, 95% CI 1.82–4.39), Caesarean section (ES 1.47, 95% CI 1.20–1.79), and parental age >35 years (mothers ES 1.97, 95% CI 1.45–2.68; fathers ES 1.33, 95% CI 0.99–1.79) were observed to be associated with hepatoblastoma. Paternal smoking during preconception/pregnancy was associated with an increased risk of hepatoblastoma (ES = 1.58, 95% CI 1.18–2.12). Paternal occupational exposure to pesticides during preconception/pregnancy was associated with an increased risk of retinoblastoma (ES = 1.55, 95% CI 1.09–2.21). For some other exposures, we found several raised ES but with very wide CIs.
Discussion
We identified only a few modifiable risk factors for certain childhood cancers, notably paternal smoking for hepatoblastoma and paternal occupational exposure to pesticides for retinoblastoma. Larger studies for rare childhood cancers are needed, with international collaboration to increase sample sizes.
Keywords: paternal smoking, pesticides, rare cancer, solid childhood cancer, systematic review and meta-analysis
Introduction
Globally, retinoblastoma, hepatoblastoma, germ cell tumors, bone tumors, and soft tissue tumors are considered rare childhood cancers, each with an incidence rate below one per 100,000 children per year (1–6).
Retinoblastoma is an aggressive cancer of the retina and occurs more often unilaterally than bilaterally. It occurs slightly more frequently in male children than in female ones, with an estimated male-to-female ratio of 1.3:1.00. Retinoblastoma typically peaks at 1 to 2 years of age for sporadic (usually unilateral) cases, whereas bilateral retinoblastoma, often heritable, peaks earlier at around 9–12 months (7–9). The 5-year survival rate is approximately 95% in high-income countries (HICs), largely due to early detection and access to chemotherapy (10, 11). In contrast, survival in low- and middle-income countries (LMICs) ranges from 30% to 60%, primarily because of delayed presentation and limited access to treatment (12). Clinically, leukocoria is the most common presenting sign, occurring in approximately 56% of cases, followed by strabismus in approximately 20% (13).
Hepatoblastoma is the most common malignant tumor in the liver accounting for 90% of pediatric hepatic tumors. Countries such as the United States, Japan, and those in Western Europe demonstrate higher reported incidence rates, partly due to more complete surveillance and comprehensive registries (14, 15). It occurs predominantly in children under 5 years of age and shows a male predilection, with an estimated male-to-female ratio ranging from 1.2:1 to 3.6:1 (16, 17). Due to significant medical and surgical advancements in recent years, the overall survival of low-risk hepatoblastoma has improved markedly from approximately 30% to 90%. In contrast, high-risk patients, particularly those with metastatic disease, older age at diagnosis, or bilobar liver involvement, experience much poorer outcomes, often with survival rates below 50%. These outcomes are even lower in LMICs (18, 19).
Unlike the other tumor types, germ cell tumors are a heterogenous group occurring at various anatomical sites. Malignant germ cell tumors are rare, accounting for approximately 3%–5% of childhood neoplasms, with an estimated male-to-female ratio of 0.8:1 (20, 21). Although it is predominantly localized in the gonads, they can also occur in extragonadal sites, particularly in children <6 years (22). Childhood ovarian germ cell tumors show a peak incidence in early adolescence, whereas childhood testicular germ cell tumors exhibit two distinct age peaks: children younger than 3 years, who may present with mature teratomas or malignant germ cell tumors, and adolescents, who may develop seminomas or mixed malignant tumors (23). An increasing incidence of malignant testicular germ cell tumors has been reported in many countries, particularly in Northern and Western Europe. In contrast, incidence trends for ovarian germ cell tumors vary, with studies reporting both increases and decreases over time (21, 24–28). In HICs, testicular germ cell tumors have an excellent prognosis, with an overall 5-year relative survival of approximately 95%. For localized testicular cancer, the 5-year survival rate exceeds 99% (29). Data are sparse for LMICs, with survival rates generally lower.
Malignant bone tumors account for approximately 3% of childhood and adolescent cancers. Osteosarcoma and the Ewing sarcoma family of tumors are the most common malignant bone tumors, together representing the majority of cases (30). Osteosarcoma and Ewing sarcoma in children have a peak incidence in the second decade of life (31–34). The overall male-to-female ratio is approximately 1.3:1. The 5-year overall survival for childhood bone tumors is around 60% in HICs (35–37) but is substantially lower in LMICs, ranging from 20% to 40% (37, 38).
Similarly, soft tissue tumors also peak in the second decade of life. Soft tissue sarcomas account for approximately 7% of all childhood cancers and are broadly classified into two main types: rhabdomyosarcoma and non-rhabdomyosarcoma soft tissue sarcomas.
Rhabdomyosarcoma is the most common soft tissue sarcoma in children and is a high-grade malignancy composed of cells resembling skeletal myoblasts (39). Notably, soft tissue tumors show a higher prevalence in male patients, with an approximate male-to-female ratio of 1.5:1 (40). The 5-year overall survival for malignant soft tissue tumors is around 65% in HICs, compared with approximately 30% in LMICs (41, 42).
The etiology of these rare childhood cancers remains largely unknown. Risk factors investigated in relation to childhood cancers included assisted reproductive technology (ART), Caesarean section (C-section), gestational age, small for gestational age (SGA), large for gestational age (LGA), birth weight, parental age, gestational diabetes, paternal smoking, pesticide use, and parental occupational exposures, all of which have been hypothesized to increase the risk for childhood cancers (43–49). The aim of this systematic review and meta-analysis is to synthesize and elucidate evidence from different epidemiological studies on the risk factors associated with retinoblastoma, hepatoblastoma, germ cell tumors, bone tumors, and soft tissue tumors, which may inform primary prevention. Although the primary focus of this review was on modifiable risk factors, we additionally included other non-modifiable risk factors to provide a more comprehensive overview of factors associated with these rare childhood cancers.
Materials and methods
Search strategies and selection criteria
We used the Preferred Reporting Items for Systematic Reviews and Meta-Analyses (PRISMA) 2020 checklist to conduct the systematic review and meta-analysis (50) (Supplementary Material, pages 3–5). The search strategy used for article identification and the methods for data extraction and analysis have been previously reported (51, 52). The databases used in this study were PubMed, Web of Science, and Embase, with no restrictions on publication date and language.
Inclusion and exclusion criteria
We extracted information from included articles published between 1988 and 2024. The studies included were case–control or cohort studies of cancer (retinoblastoma, hepatoblastoma, germ cell tumors, bone tumors, and soft tissue tumors) diagnosed in children and adolescents under the age of 20 years, from which we extracted exposure time windows and estimates of relative risks (RRs), such as odds ratio (OR), hazard ratio, standardized mortality ratio, mortality rate ratio, standard incidence ratio, or incidence rate ratio with 95% confidence intervals (CIs). We checked publications from the same region for overlaps of their study populations. The inclusion and exclusion criteria were defined a priori (Supplementary Material, page 2) (51, 52).
Study selection and data extraction
Identified peer reviewed articles were retrieved and screened for duplicates in EndNote version X9.3.3. The authors, FMO and RD, assessed the titles, abstracts, and full text of the articles independently to determine their eligibility (53). Disagreements arising from the independent selection process were resolved by seeking the opinion of the third and last authors, AO and JS. Additional articles were sourced from the lists of references of the selected articles. We structured our search strategy in line with population, exposure, comparator, and outcome (PECO) components and included a list of keywords and MeSH terms (Supplementary Material, pages 6–11). The search was initially conducted in June 2022 and subsequently updated until January 2025 (we reran the original search strategy using the same databases and search terms but looking from the end of the previous search to January 2025).
Risk factors extracted included birth and parental characteristics, occupational exposures to pesticides, wood dust, paint, gasoline fumes and livestock/animals, and lifestyle exposures including maternal diet, vitamin intake, parental smoking, and alcohol consumption. Others were maternal medical radiation exposure, residential proximity to major roads, and childhood exposure to traffic density. Exposure time period such as preconceptional, prenatal, and postnatal were also extracted. Other information extracted include author names, year of publication, study location, period and age range of diagnosis, exposure assessment methods, outcome ascertainment, number of childhood cancer cases and controls or, if not available, the study population, follow-up duration, and risk estimates with their respective 95% CIs. Information regarding study design (case–control and cohort or nested case–control) was also extracted. Registry-based case–control studies were considered as cohort design in the present analysis, as usually nested within a nationwide registry landscape and therefore similar, in design, to those case–control studies nested within cohorts (51). Case–control studies are thereby studies requiring interaction with the study participants.
Assessment of study quality
All eligible articles underwent a quality assessment of their methodological quality using the Joanna Briggs Institute (JBI) critical appraisal tools for case–control and cohort studies (54). The appraisal checklist has 10 criteria for case–control and 11 for cohort studies. Every question answered with a “yes” received a score of 1, while a “no” scored 0 and “unclear” or “not applicable” also received 0 (Supplementary Material, pages 12–15). Prior to the critical appraisal of the articles, we systematically checked the articles for overlaps by study population and by risk factors.
Statistical analyses
We performed random-effects meta-analyses in order to estimate pooled effect sizes (ES) with their respective 95% CIs. Funnel plots and Egger’s test were employed to assess potential publication bias (55). I2 statistic was calculated to quantify the heterogeneity of the results between studies. I2 values of 0% were considered to represent “no heterogeneity”, 1%–35% as “low heterogeneity”, 36%–55% as “moderate”, 56%–70% as “substantial”, and above 71% as “considerable” heterogeneity (56). Analyses were conducted by combining both case–control and cohort studies and separately by study design (case–control vs. cohort studies/nested case–control studies). The combined analysis of cohort and case–control studies was presented as the primary focus, unless otherwise stated. The rationale to combine these studies in the primary analysis was based on the limited number of available studies for several risk factors, with the aim of maximizing statistical power and providing a more comprehensive synthesis of the evidence. In addition, while acknowledging that the different designs have their own strengths and weaknesses, all included studies were conducted with the same objective to identify risk factors, hence combined in the first step and stratified in the second step to explore consistency across study designs. Meta-analyses were only performed when at least two studies were available for a given risk factor, and assessments of publication bias were conducted only when at least three studies were included. For risk factors with only one available study, the results were described narratively. Analyses were conducted using STATA® software, version 15.1 (College Station, TX, USA) using a nominal significance level of 0.05.
Results
A total of 3,772 unique records were retrieved and screened, leading to the evaluation of 96 full texts. Among these, 75 articles from 59 independent studies (31 articles from 22 case–control studies and 44 articles from 37 cohort studies) met the study inclusion criteria (Figure 1; Tables 1, 2).
Figure 1.

Preferred reporting items for systematic reviews and meta-analyses flow diagram outlining the article selection.
Table 1.
Characteristics of the 44 cohort studies and registry-based case-control studies included in the systematic review and meta-analysis, sorted by country.
| First author | Study design | Country | Date of diagnoses | Age (years) | Risk factor | Data source | Outcome ascertainment | Solid tumor type | Cases | Study population | Follow-up (years) |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Oceania | |||||||||||
| Stavrou et al., 2009 (57) | CO | Australia | 1994–2005 | <13 | Maternal smoking | Midwives’ data collection | Cancer registry | Retinoblastoma, hepatoblastoma, and germ cell | 260 | 979,809 | NA |
| Asia | |||||||||||
| Heck et al., 2020 (58) | CO | China–Taiwan | 2004–2014 | <12 | Gestational risk factors | Hospital records | Cancer registry | Retinoblastoma, hepatoblastoma, and germ cell | 614 | 2,079,037 | NA |
| Huang et al., 2022 (59) | RBCC | China–Taiwan | 2004–2014 | <12 | Gestational diabetes | Hospital records | Cancer registry | Retinoblastoma, hepatoblastoma, and germ cell | 2,160 | 2,076,877 | NA |
| Weng et al., 2022 (60) | CO | China–Taiwan | 2004–2017 | <14 | Assisted reproductive technology (ART) | National databases | Cancer registry | Retinoblastoma and hepatoblastoma | 273 | 2,308,016 | 11 |
| Cha et al., 2011 (61) | CO | Korea | 1995–2006 | <12 | Birth characteristics | Birth database | Death database | Hepatoblastoma, retinoblastoma, and soft tissue | 189 | 6,479,406 | 11 |
| Europe | |||||||||||
| Momen et al., 2016 (62) | CO | Denmark | 1996–2008 | <15 | Maternal smoking | National patient register | Cancer registry | Retinoblastoma and bone | 160 | 888,556 | 15 |
| Rios et al., 2024 (63) | CO | France | 2010–2021 | <15 | ART | French National Mother–Child Register | French national registry of childhood cancer | Retinoblastoma and soft tissue | 21 | 8,526,306 | 10.9 |
| Volk et al., 2020 (64) | RBCC | Denmark | 1968–2016 | <19 | Parental occupational exposure | Employment history from civil registration system | Cancer registry | Hepatoblastoma and retinoblastoma | 64 | 1,116 | 18 |
| Schüz et al., 2015 (65) | CO | Denmark | 1973–2010 | <20 | Birth order | Population and birth registers | Cancer registry | Retinoblastoma, hepatoblastoma, bone, and soft tissue | 1,068 | 2,461,283 | 20 |
| Contreras et al., 2017 (66) | RBCC | Denmark | 1968–2015 | <16 | Parental age | Birth certificates | Cancer registry | Retinoblastoma, germ cell, and soft tissue | 1,310 | 585,594 | 15 |
| Hall et al., 2020 (67) | RBCC | Denmark | 1968–2016 | <17 | Occupational livestock or animal dust | Birth registry and parental occupational history | Cancer registry | Retinoblastoma and soft tissue | 32 | 6,393 | 16 |
| Hall et al., 2021 (68) | RBCC | Denmark | 1968–2015 | <16 | Parental occupation | Birth registry and parental occupational history | Cancer registry | Germ cell tumor | 178 | 4,355 | 15 |
| Sundh et al., 2014 (69) | CO | Denmark | 1968–2004 | <15 | ART | Hospital records | Cancer registry | Retinoblastoma, hepatoblastoma, soft tissue, bone, and germ cell | 138 | 450,215 | 9.5 mean |
| Momen et al., 2014 (70) | CO | Denmark, Sweden, and Finland | 1973–2007 | <15 | Delivery by caesarean section | Birth registry | Cancer registers | Retinoblastoma, hepatoblastoma, bone, and germ cell | 1,515 | 7,029,843 | 15 |
| Seppälä et al., 2021 (71) | RBCC | Finland | 1996–2014 | <20 | Preterm birth | Medical records | Cancer registry | Retinoblastoma, hepatoblastoma, soft tissue, bone, and germ cell | 140 | 1,888 | 19 |
| de Fine Licht et al., 2012 (72) | RBCC | Nordic countries | 1985–2006 | <15 | Multiple risk factors | Birth registry | Cancer registry | Hepatoblastoma | 155 | 775 | 14 |
| Stephansson et al., 2011 (73) | RBCC | Nordic countries | 1967–2006 | <15 | Multiple risk factors | Birth registry | Cancer registry | Germ cell | 152 | 1,520 | 14 |
| Bjørge et al., 2013 (74) | RBCC | Nordic countries | 1967–2010 | <15 | Fetal growth | Birth registry | Cancer registries and in direct reports from pediatric, oncology, and neurosurgery hospitals | Retinoblastoma, bone, and soft tissue | 2,779 | 172,422 | 14 |
| Mortensen et al., 2016 (75) | CO | Norway | 1999–2010 | <15 | Folic acid in pregnancy | Birth registry | Cancer registry | Bone and soft tissue | 189 | 687,406 | 6 |
| Pershagen et al., 1992 (76) | CO | Sweden | 1982–1987 | <6 | Maternal smoking | Birth registry | Cancer registry | Soft tissue | 15 | 148,917 | 5 |
| Yip et al., 2006 (77) | CO | Sweden | 1961–2000 | <15 | Parental age | Multi-generation register | Cancer registry | Retinoblastoma | 574 | 4.3 million | 14 |
| Rossides et al., 2022 (78) | RBCC | Sweden | 1960–2015 | <20 | Parental occupational exposure to hydrocarbon solvents and engine exhaust fumes |
Employment history and job exposure matrix | Cancer registry | Retinoblastoma and hepatoblastoma | 1,161a | 172,194 a | 19 |
| Coste et al., 2020 (79) | CO | Switzerland | 1990–2015 | <16 | Parental occupational exposure to pesticides | Census records/CLIC-JEM | Cancer registry | Bone, soft tissue, and germ cell | 593 | 3.5 million | 15 |
| MacCarthy et al., 2009 (80) | RBCC | UK | 1962–1999 | <15 | Paternal occupational exposures | Occupational and birth records | National registry | Retinoblastoma | 1,318 | 1,318 | 14 |
| Williams et al., 2013 (81) | CO | UK | 1992–2008 | <15 | ART | Human Fertilization and Embryology Authority records | Cancer registry | Bone and germ cell | 35 | 106,013 | 7 |
| Williams et al., 2018 (82) | CO | UK | 1992–2008 | <15 | ART | Human Fertilization and Embryology Authority records | Cancer registry | Retinoblastoma and hepatoblastoma | 12 | 12,137 | 8 |
| Dockerty et al., 2001 (83) | RBCC | UK | 1968–1986 | <15 | Parental age | Birth records | National Registry of Childhood Tumors | Retinoblastoma | 415 | 10,868 | 14 |
| Fear et al., 1998 (84) | CO | UK | 1959–1990 | <15 | Occupational exposure to pesticide | Death certificates | National Statistics | Bone and soft tissue | 66 | 167,703 | 14 |
| Kendall et al., 2020 (85) | RBCC | UK | 1962–2010 | <15 | Paternal occupational exposures | Birth/employment records and job exposure matrix | National registry of Childhood Tumors | Bone and soft tissue | 5,369 | 5,380 | 14 |
| North America | |||||||||||
| Marcoux et al., 2022 (86) | CO | Canada—Quebec | 2006–2019 | <14 | Gestational diabetes | Hospital records | Cancer registry | Retinoblastoma, hepatoblastoma, and soft tissue | 61 | 1,030,537 | 14 |
| Spector et al., 2019 (87) | CO | USA | 2004–2012 | <10 | In vitro fertilization | Hospital records | Cancer registry | Retinoblastoma, hepatoblastoma, soft tissue, and germ cell | 59 | 275,686 | 8 |
| Hall et al., 2019 (88) | RBCC | USA—California | 1984–2013 | <6 | Prenatal exposure to air toxics | Birth certificates and air measurement | Cancer registry | Germ cell | 243 | 147,100 | 5 |
| Thompson et al., 2022 (45) | RBCC | USA—California | 1988–2013 | <16 | Prenatal pesticide exposure | Addresses on birth certificate and geocode | Cancer registry | Retinoblastoma | 335 | 123,166 | 15 |
| Williams et al., 2021a (89) | RBCC | USA—Minnesota | 1976–2014 | <15 | Caesarean section | Birth certificate | Cancer registry | Retinoblastoma, hepatoblastoma, bone, and soft tissue | 3,166a | 20,589 | 14 |
| Williams et al., 2021b (90) | RBCC | USA—Minnesota, California, New York, Texas, and Washington | 1976–2014 | <15 | Birth characteristics | Birth certificate | Cancer registry | Hepatoblastoma and soft tissue | 16,411a | 69,816 | 14 |
| McLaughlin et al., 2006 (91) | RBCC | USA—New York | 1985–2001 | <6 | Maternal and infant birth characteristics | Birth certificates | Cancer registry | Hepatoblastoma | 58 | 116 | 5 |
| Shakeel et al., 2020 (92) | RBCC | USA and Canada | 1998–2006 | <13 | Medical radiation | Dose estimation using X-ray energy | Children’s Oncology Group | Retinoblastoma | 482 | 404 | 12 |
| Contreras et al., 2016 (93) | RBCC | USA—California | 1988–2013 | <6 | Gestational diabetes | Birth records | Cancer registry | Retinoblastoma and hepatoblastoma | 3,508 | 270,147 | 5 |
| Morimoto et al., 2016 (94) | RBCC | USA—California | 1988–2011 | <20 | Birth characteristics | Birth certificates | Cancer registry | Soft tissue | 722 | 2,888 | 19 |
| Heck et al., 2012 (95) | RBCC | USA—California | 1988–2007 | <6 | Perinatal characteristics | Birth certificate | Cancer registry | Retinoblastoma | 609 | 209,051 | 5 |
| Heck et al., 2013 (96) | RBCC | USA—California | 1988–2007 | <6 | Birth characteristics | Birth certificates | Cancer registry | Hepatoblastoma | 261 | 218,277 | 5 |
| Kumar et al., 2018 (97) | RBCC | USA—Texas | 2003–2009 | <5 | Maternal residential proximity to major roadways | Texas roadway network StratMap | Cancer registry | Retinoblastoma and hepatoblastoma | 144 | 2,855 | 4 |
| Flower et al., 2004 (98) | CO | USA—Iowa and North Carolina | 1975–1998 | <19 | Paternal occupational exposures to pesticides | Birth certificate | Cancer registry | Retinoblastoma, bone, soft tissue, and germ cell | 50 | 17,357 | 18 |
| Carozza et al., 2009 (99) | RBCC | USA—Texas | 1990–1998 | <15 | Pesticides | Digital orthophoto quadrangle (DOQ) data | Cancer registry | Germ cell | 696 | 1,802 | 14 |
CO, cohort studies; RBCC, registry-based case–control studies; NA, not available.
aCase/study population combined with other risk factors.
Table 2.
Characteristics of the 31 case-control studies included in the systematic review and meta-analysis, sorted by country.
| First author | Country | Date of diagnoses | Age (years) | Risk factor | Exposure assessment | Outcome ascertainment | Solid tumor type | Cases | Control | |
|---|---|---|---|---|---|---|---|---|---|---|
| Latin America | ||||||||||
| Rios et al., 2018 (46) | Peru | 2012–2015 | <18 | Parental age | Self-administered questionnaire and hospital records | Hospital records | Retinoblastoma, hepatoblastoma, bone and soft tissue | 166 | 332 | |
| Europe | ||||||||||
| Hug et al., 2010 (100) | Germany | 1992–1994 | <15 | Parental occupational exposure to extremely low frequency magnetic fields (ELF-MF) | Self-administered questionnaire and telephone interview | Cancer registry | Bone and soft tissue | 600 | 2,382 | |
| Schüz and Forman, 2007 (101) | Germany | 1992–1994 | <14 | Birth weight by gestational age | Self-administered questionnaire and telephone interview | Cancer registry | Bone and soft tissue | 541 | 2,057 | |
| Schüz et al., 2007 (102) | Germany | 1992–1994 | <14 | Medication use during pregnancy | Self-administered questionnaire and telephone interview | Cancer registry | Bone and soft tissue | 234 | 2,057 | |
| Schüz et al., 1999 (103) | Germany | 1992–1994 | <15 | Parental smoking | Self-administered questionnaire and telephone interview | Cancer registry | Bone and soft tissue | 217 | 3,659 | |
| Hardell and Dreifaldt, 2001 (104) | Sweden | 1988–1991 | <15 | Breast feeding | Medical records | Cancer registry | Retinoblastoma, hepatoblastoma, bone and soft tissue | 181 | 860 | |
| Sorahan et al., 1997 (105) | UK | 1953–1955 | <16 | Parental smoking | Face-to-face interview | Birth registry | Bone | 293 | 293 | |
| Sorahan and Lancashire, 2004 (49) | UK | 1953–1955, 1971–1976, 1977–1981 | <16 | Parental smoking | Face-to-face interview | Birth registry | Hepatoblastoma | 43 | 5,777 | |
| Smith et al., 2009 (106) | UK | 1991–1996 | <15 | Birth weight | Face-to-face interview | Cancer registry | Retinoblastoma, hepatoblastoma, and germ cell | 3,651 | 6,337 | |
| Pang et al., 2003 (107) | UK | 1991–1994 | <15 | Parental smoking | Face-to-face interview | Cancer registry | Retinoblastoma, hepatoblastoma, germ cell, bone, and soft tissue tumors | 1,378 | 7,629 | |
| Rajaraman et al., 2011 (108) | UK—England and Wales | 1992–1996 | <15 | Diagnostic radiation | Face-to-face interview | Histopathology review database or individual consultant | Retinoblastoma, hepatoblastoma, and soft tissue | 240 | 4,857 | |
| North America | ||||||||||
| Shu et al., 1995 (109) | United States and Canada | 1982–1989 | <15 | Multiple risk factors | Self-administered questionnaire | Children’s cancer group | Germ cell | 105 | 639 | |
| Chen et al., 2005 (110) | USA | 1993–2001 | <15 | Parental smoking and drinking | Self-administered questionnaire and telephone interview | Children’s cancer group | Germ cell | 274 | 421 | |
| Chen et al., 2006 (111) | USA | 1993–2001 | <15 | Exposure to residential pesticides, chemicals, dusts, fumes, and metals | Self-administered questionnaire and telephone interview | Children’s cancer group | Germ cell | 272 | 418 | |
| Musselman et al., 2011 (112) | USA | 2000–2008 | <6 | Birth characteristics | Telephone interview | Children’s Oncology Group | Germ cell | 222 | 336 | |
| Musselman et al., 2013 (113) | USA | 2000–2008 | <6 | Maternal pregnancy events | Telephone interview | Children’s Oncology Group | Hepatoblastoma | 383 | 387 | |
| Janitz et al., 2017 (114) | USA | 2000–2008 | <6 | Parental occupational exposures | Telephone interview | Children’s Oncology Group | Hepatoblastoma | 383 | 387 | |
| Johnson et al., 2008 (115) | USA and Canada | 2000–2008 | <16 | Maternal vitamin intake | Telephone interview | Children’s Oncology Group | Germ cell | 278 | 423 | |
| Johnson et al., 2013 (116) | USA and Canada | 2000–2008 | <6 | Parental tobacco and alcohol consumption | Telephone interview | Children’s Oncology Group | Hepatoblastoma | 383 | 387 | |
| Omidakhsh et al., 2017 (117) | USA and Canada | 2006–2012 | <16 | Residential pesticide exposures | Telephone interview | Children’s Oncology Group | Retinoblastoma | 282 | 564 | |
| Omidakhsh et al., 2018 (118) | USA and Canada | 2006–2012 | <16 | Parental occupational exposures | Telephone interview | Children’s Oncology Group | Retinoblastoma | 187 | 157 | |
| Heck et al., 2015 (119) | USA and Canada | 2006–2011 | <15 | Perinatal characteristics | Telephone interview | Children’s Oncology Group | Retinoblastoma | 282 | 146 | |
| Azary et al., 2016 (120) | USA and Canada | 2011–2013 | <15 | Parental smoking and alcohol consumption | Telephone interview | Children’s Oncology Group | Retinoblastoma | 488 | 424 | |
| Lombardi et al., 2015 (121) | USA and Canada | 2006–2012 | <16 | Maternal diet | Telephone interview | Cancer registry | Retinoblastoma | 163 | 136 | |
| Abdolahi et al., 2013 (122) | USA and Canada | 1998–2006 | <14 | Paternal occupational exposures | Telephone interview | Cancer registry | Retinoblastoma | 135 | 245 | |
| John et al., 1991 (123) | USA—Colorado | 1976–1983 | <15 | Parental smoking | Face-to-face and telephone interview | Cancer registry | Soft tissue | 26 | 196 | |
| Yeazel et al., 1997 (124) | USA—California | 1982–1989 | <2 | Birth weight | Self-administered questionnaire | Children’s cancer group | Soft tissue | 531 | 816 | |
| Savitz and Kaune, 1993 (125) | USA—Colorado | 1976–1983 | <15 | Residential wire code | Face-to-face and telephone interview | Cancer registry | Soft tissue | 32 | 260 | |
| Savitz and Ananth, 1994 (126) | USA—Colorado | 1976–1983 | <15 | Birth characteristics | Face-to-face and telephone interview | Cancer registry | Soft tissue | 26 | 212 | |
| Savitz et al., 1988 (127) | USA—Colorado | 1976–1983 | <15 | Magnetic fields | Face-to-face and telephone interview | Cancer registry | Soft tissue | 32 | 26 | |
| Savitz and Feingold, 1989 (128) | USA—Colorado | 1976–1983 | <15 | Traffic density | Face-to-face and telephone interview | Cancer registry | Soft tissue | 32 | 262 | |
Among all of the articles that met the criteria, 47% (n = 35) were carried out in North America. Europe came next with 45% (n = 34), followed by Asia with 5% (n = 4) and Oceania and Latin America with 1% (n = 1) each, respectively. There were no eligible studies in Africa. All publications that met the criteria were in English language.
Study bias and quality assessment
The 75 articles critically appraised for quality using the JBI tools were of good quality (84%). The case–control studies had a slightly higher average score (86%) compared to cohort studies (81%). The least ranked case–control study scored 7 out of 10 points, while for the cohort study it was 7 out of 11 points. Thus, all screened articles appraised were included in the final analysis (Supplementary Material, pages 12–15).
Retinoblastoma
Low birth weight (<2,500 g) showed a borderline association with the risk of retinoblastoma (ES 1.27, 95% CI 0.99–1.63) based on estimates from one case–control study and three cohort studies. The RR for ART was elevated, but with a wide confidence interval, based on estimates from five cohort studies which were consistently above 1.00, except for the study by Sundh and co-authors (69). Gestational age (<37 and >40 weeks) and gestational diabetes also showed elevated risks, but with wide confidence intervals. Breastfeeding (≥6 months), C-section, “small and large for gestational age” (SGA and LGA), high birth weight (>4,000 g), younger parents (<25 years), and older parents (>35 years) were not associated with retinoblastoma risk. The funnel plots were symmetric for the risk factors assessed (Figure 2; Table 3; Supplementary Material, pages 16–21), suggesting no publication bias.
Figure 2.

Meta-analysis of pooled effect sizes (ES) of exposure to (A) low (<2,500 g) and (B) high (>4,000 g) birth weight compared with normal birth weight (2.5–4 kg) for the risk of various childhood cancer types and heterogeneity by study design. †, risk estimate not ES, as only one study was identified.
Table 3.
Meta-analysis of pooled effect sizes (ES) of birth and parental characteristics, and paternal occupational exposures for the risk of childhood cancer and heterogeneity (I2) between studies by study design.
| Risk factors | Study design | Retinoblastoma | n | I2 (%) | Hepatoblastoma | n | I2 (%) | Bone | n | I2 (%) | Germ cell | n | I2 (%) | Soft tissue | n | I2 (%) | ||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| ES [95% CI] | ES [95% CI] | ES [95% CI] | ES [95% CI] | ES [95% CI] | ||||||||||||||||||||||
| ART | Cohort | 1.27 | 0.75 | 2.16 | 5 | 44.5 | 2.82 | 1.82 | 4.39 | 4 | 0.0 | 1.18 | 0.62 | 2.23 | 4 | 20.0 | 1.29 | 0.89 | 1.87 | 4 | 0.0 | |||||
| Caesarean section | Case–control | 0.50 | 0.21 | 1.19 | 1 | – | 1.31 | 0.82 | 2.07 | 1 | – | 0.85 | 0.50 | 1.45 | 1 | – | ||||||||||
| Cohort | 0.91 | 0.54 | 1.55 | 3 | 50.5 | 1.47 | 1.20 | 1.79 | 4 | 0.0 | 0.91 | 0.47 | 1.78 | 2 | 61.9 | 1.00 | 0.57 | 1.73 | 1 | – | 0.77 | 0.44 | 1.35 | 1 | – | |
| Combined | 0.78 | 0.42 | 1.42 | 3 | 62.1 | 1.17 | 0.82 | 1.67 | 2 | 0.0 | 0.81 | 0.55 | 1.19 | 2 | 0.0 | |||||||||||
| Gestational age <37 weeks | Case–control | 1.20 | 0.80 | 1.90 | 1 | – | 6.10 | 1.60 | 23.40 | 1 | – | |||||||||||||||
| Cohort | 1.43 | 0.89 | 2.29 | 4 | 49.1 | 1.90 | 0.92 | 0.94 | 7 | 84.9 | 1.11 | 0.74 | 1.66 | 3 | 0.0 | 0.87 | 0.66 | 1.15 | 2 | 0.0 | ||||||
| Combined | 1.15 | 0.85 | 1.54 | 4 | 0.0 | 1.41 | 0.60 | 3.31 | 3 | 75.5 | ||||||||||||||||
| Gestational age >40 weeks | Case–control | 1.00 | 0.60 | 1.50 | 1 | – | 0.40 | 0.10 | 1.80 | 1 | – | |||||||||||||||
| Cohort | 1.39 | 0.58 | 3.32 | 2 | 43.1 | 1.13 | 0.82 | 1.56 | 4 | 0.0 | 1.10 | 0.66 | 1.83 | 1 | – | 0.82 | 0.68 | 0.98 | 1 | – | ||||||
| Combined | 1.04 | 0.74 | 1.47 | 2 | 0.0 | 0.81 | 0.68 | 0.97 | 2 | 0.0 | ||||||||||||||||
| SGA | Case–control | 1.10 | 0.53 | 2.10 | 1 | – | 0.87 | 0.31 | 2.47 | 2 | 76.5 | 1.06 | 0.72 | 1.57 | 2 | 0.0 | ||||||||||
| Cohort | 1.07 | 0.83 | 1.39 | 1 | – | 1.76 | 1.28 | 2.43 | 2 | 0.0 | 1.00 | 0.76 | 1.32 | 1 | – | |||||||||||
| Combined | 1.07 | 0.84 | 1.37 | 2 | 0.0 | 1.02 | 0.81 | 1.28 | 3 | 0.0 | ||||||||||||||||
| LGA | Case–control | 1.09 | 0.83 | 1.43 | 1 | – | 1.03 | 0.62 | 1.72 | 2 | 0.0 | 1.26 | 0.45 | 3.50 | 2 | 75.3 | ||||||||||
| Cohort | 0.77 | 0.33 | 1.80 | 1 | – | 1.51 | 0.86 | 2.65 | 2 | 0.0 | 0.94 | 0.72 | 1.23 | 1 | – | |||||||||||
| Combined | 1.06 | 0.81 | 1.37 | 2 | 0.0 | 1.10 | 0.66 | 1.85 | 3 | 61.8 | ||||||||||||||||
| Maternal age <25 | Case–control | 1.02 | 0.07 | 14.12 | 1 | – | 1.00 | 0.80 | 1.40 | 1 | – | |||||||||||||||
| Cohort | 1.15 | 0.83 | 1.59 | 4 | 0.0 | 1.40 | 0.90 | 2.18 | 5 | 47.2 | 1.02 | 0.66 | 0.66 | 2 | 0.0 | 0.84 | 0.68 | 1.04 | 3 | |||||||
| Combined | 1.40 | 0.93 | 2.10 | 6 | 34.7 | 1.01 | 0.80 | 1.27 | 3 | 0.0 | 0.0 | |||||||||||||||
| Maternal age >35 | Case–control | 1.08 | 0.55 | 2.10 | 2 | 0.0 | 4.35 | 0.31 | 60.38 | 1 | – | 1.10 | 0.70 | 1.60 | 1 | – | 1.59 | 0.45 | 8.59 | 1 | – | |||||
| Cohort | 1.19 | 0.82 | 1.74 | 4 | 17.4 | 1.95 | 1.43 | 2.66 | 2 | 0.0 | 1.40 | 0.93 | 2.11 | 2 | 0.0 | 0.63 | 0.38 | 1.04 | 1 | – | ||||||
| Combined | 1.15 | 0.85 | 1.57 | 6 | 0.0 | 1.97 | 1.45 | 2.68 | 3 | 0.0 | 1.24 | 0.93 | 1.66 | 3 | 0.0 | 0.76 | 0.37 | 1.60 | 2 | 26.3 | ||||||
| Paternal age <25 | Case–control | 1.10 | 0.70 | 1.70 | 1 | – | ||||||||||||||||||||
| Cohort | 0.85 | 0.56 | 1.29 | 4 | 46.7 | 1.11 | 0.65 | 1.91 | 4 | 43.1 | 0.79 | 0.44 | 1.44 | 1 | – | |||||||||||
| Combined | 0.98 | 0.69 | 1.39 | 2 | 0.0 | |||||||||||||||||||||
| Paternal age >35 | Case–control | 1.30 | 0.50 | 3.60 | 1 | 0.0 | 0.10 | 0.01 | 1.80 | 1 | – | 1.10 | 0.90 | 1.30 | 1 | – | 0.39 | 0.12 | 1.30 | 1 | – | |||||
| Cohort | 0.97 | 0.71 | 1.33 | 4 | 0.0 | 1.34 | 1.07 | 1.67 | 6 | 0.0 | 0.77 | 0.45 | 1.30 | 2 | 47.0 | 1.14 | 0.78 | 1.66 | 1 | – | ||||||
| Combined | 0.99 | 0.74 | 1.34 | 5 | 0.0 | 1.33 | 0.99 | 1.79 | 7 | 25.5 | 0.92 | 0.64 | 1.32 | 3 | 57.8 | 0.78 | 0.29 | 2.13 | 2 | 64.7 | ||||||
| Gestational diabetes | Case–control | |||||||||||||||||||||||||
| Cohort | 1.35 | 0.93 | 1.96 | 2 | 0.0 | 1.35 | 0.86 | 2.14 | 3 | 0.0 | ||||||||||||||||
| Combined | ||||||||||||||||||||||||||
| Paternal occupational exposure | ||||||||||||||||||||||||||
| Paternal occupational exposure to wood dust | Cohort | 1.26 | 0.74 | 2.15 | 2 | 0.0 | ||||||||||||||||||||
| Paternal occupational exposure to paint | Case–control | 1.04 | 0.35 | 3.13 | 2 | 46.5 | ||||||||||||||||||||
| Cohort | 6.00 | 0.73 | 276.00 | 1 | – | |||||||||||||||||||||
| Combined | 1.33 | 0.43 | 4.15 | 3 | 43.2 | |||||||||||||||||||||
| Paternal occupational exposure to gasoline fumes | Case–control | 1.29 | 0.64 | 2.60 | 2 | 0.0 | ||||||||||||||||||||
| Paternal occupational livestock/animal exposure | Cohort | 0.99 | 0.44 | 2.22 | 2 | 56.2 | ||||||||||||||||||||
The ES for maternal smoking during pregnancy was elevated but with a wide confidence interval, including 1.00 for the risk of retinoblastoma. This was based on the combined estimates from two cohort studies and two case–control studies. Paternal exposure to smoking during preconception/pregnancy and the risk of retinoblastoma did not show evidence of an association based on estimates from two case–control studies only.
Paternal occupational exposure to pesticides during preconception/pregnancy was associated with the risk of retinoblastoma (ES 1.55, 95% CI 1.09–2.21) based on estimates from two case–control and two cohort studies. No heterogeneity was observed across studies. Similarly, maternal residential exposure to pesticides was associated with the risk of retinoblastoma in one cohort study (45). Paternal occupational exposure to wood dust showed an elevated risk of retinoblastoma based on estimates from two cohort studies only. Similarly, the ES of paternal occupational exposure to paint was elevated, but with a wide confidence interval based on estimates from two case–control studies and one cohort study. Maternal medical radiation history of upper and lower gastrointestinal series was associated with retinoblastoma (RR = 1.9, 95% CI: 1.1–3.2 and RR = 6.9, 95% CI: 2.9–16.4, respectively) in one cohort study (92) (Figures 3, 4; Table 3; Supplementary Material, pages 22 and 23).
Figure 3.

Meta-analysis of pooled effect sizes (ES) of exposure to (A) maternal smoking and (B) paternal smoking for the risk of various childhood cancer types and heterogeneity by study design. †, risk estimate not ES, as only one study was identified.
Figure 4.

Meta-analysis of pooled effect sizes (ES) of parental exposure to pesticides for the risk of various childhood cancer types and heterogeneity by study design. †, risk estimate not ES, as only one study was identified.
Hepatoblastoma
Low birth weight (<2,500 g) showed a threefold association with the risk of hepatoblastoma (ES 3.33 CI 1.30–8.54) based on combined estimates from one case–control study and four cohort studies. However, heterogeneity across the studies was considerable (I2 = 91.1%). ART was twofold associated with the risk of hepatoblastoma (ES 2.82, 95% CI 1.82–4.39) based on estimates from four cohort studies, with a consistent magnitude above 2.00. No heterogeneity across studies was observed. C-section was associated with an increased risk of hepatoblastoma (ES 1.47, 95% CI 1.20–1.79) based on estimates from four cohort studies, showing a consistent magnitude of association. Moderate heterogeneity was observed across studies. SGA was associated with the risk of hepatoblastoma (RR 1.76, 95% CI 1.28–2.43) based on estimates from two cohort studies. Older paternal age (>35 years) showed a borderline association with hepatoblastoma (ES 1.33, 95% CI 0.99–1.79) based on estimates from one case–control and six cohort studies. Similarly, older maternal age (ES 1.97, 95% CI 1.45–2.68) was associated with hepatoblastoma based on one case–control study and two cohort studies. Gestational age (<37 weeks) showed an elevated risk of hepatoblastoma, but with a wide confidence interval, based on estimates from seven cohort studies only. Heterogeneity across studies was considerable. LGA and gestational diabetes also showed elevated risks of hepatoblastoma, but with wide confidence intervals. These were based on two and three cohort studies, respectively. The RR of younger mothers (age <25 years) was elevated for the risk of hepatoblastoma, with a wide confidence interval. Gestational age (>40 weeks), high birth weight (>4,000 g), and young fathers (<25 years) were not associated with the risk of hepatoblastoma based on estimates from four cohort studies, one case–control study and three cohort studies, and four cohort studies, respectively (Figure 2; Table 3; Supplementary Material, pages 24–30).
Paternal smoking during preconception/pregnancy showed an increased risk of hepatoblastoma (RR 1.58, 95% CI 1.18–2.12) based on estimates from three case–control studies, with no heterogeneity across studies. On the contrary, maternal smoking during pregnancy did not show an association with the risk of hepatoblastoma based on estimates from three case–control studies and three cohort studies. Similarly, maternal vitamin intake during pregnancy did not show an association with hepatoblastoma based on estimates from one case–control study (112).
Paternal occupational exposure to gasoline fumes and the risk of hepatoblastoma was ES 1.29, 95% CI 0.64–2.60 based on estimates from two case–control studies. Maternal residential proximity within 500 m of major roadways was not associated with the risk of hepatoblastoma based on estimates from one case–control study conducted in the USA (97). The funnel plots were symmetric for all risk factors assessed except for paternal age (>35 years) (Figures 3, 4; Table 3; Supplementary Material, pages 24–30).
Bone tumors
High birth weight (>4,000 g) showed a suggestive association with an increased risk of bone tumors (ES = 1.27, 95% CI 0.98–1.64), although the confidence interval included 1.00, indicating some uncertainty. This was based on estimates from two case–control studies. However, heterogeneity across both studies was substantial (I2 = 62.1%). ART was associated with an increased risk of bone tumor (RR 2.34, 1.43–3.61) based on estimates from one case–control study. In contrast, no associations were observed between other birth characteristics (C-section, SGA, LGA, and birth weight [<2,500 g]) and the risk of bone tumors.
Parental smoking during the preconception/pregnancy period was not associated with the risk of bone tumors. Similarly, paternal occupational exposure to pesticides or to livestock/animals was not associated with the risk of bone tumors based on estimates from three and two cohort studies, respectively (Figures 2–4; Table 3; Supplementary Material, pages 30 and 31).
Germ cell tumors
Low birth weight (<2,500 g) showed a slightly elevated risk of germ cell tumors, although the wide confidence interval included 1.00, based on estimates from two case–control studies and one cohort study. Similarly, high birth weight (>4,000 g) also showed an elevated risk of germ cell tumors (ES = 1.40), but with a wide confidence interval, based on estimates from three case–control studies and one cohort study. There was no evidence of heterogeneity across studies for low birth weight (<2,500 g), whereas heterogeneity was moderate for high birth weight (>4,000 g). No significant associations were observed for ART, C-section, gestational age (<37 or >40 weeks), and parental age (<25 or >35 years) and the risk of germ cell tumors.
Maternal use of pesticides during pregnancy showed an elevated risk of germ cell tumors, but with a wide confidence interval. This was based on estimates from two case–control studies and one cohort study. A similar elevation was observed for childhood exposure to pesticides and the risk of germ cell tumors (RR 1.60); this was observed in only one cohort study (99). There were no observed associations for parental smoking, maternal alcohol consumption, maternal vitamin intake, and maternal exposure to X-ray during pregnancy and the risk of germ cell tumors, as well as between paternal occupational exposure to pesticides and the risk of germ cell tumors. These were based on estimates from three separate case–control studies, respectively (Figures 2-4; Table 3; Supplementary Material, pages 31–34).
Soft tissue tumors
Short gestational age (<37 weeks) showed an elevated risk of soft tissue tumors (ES 1.41, 95% CI, 0.60–3.31), but with a wide CI, based on one case–control and two cohort studies. No associations were observed between ART (based on four cohort studies), C-section (one case–control and one cohort study), and long gestational age (>40 weeks) (one case–control study and one cohort study) and the risk of soft tissue tumors. Similarly, no associations were observed for SGA and LGA (one case–control and two cohort studies) for birth weight <2,500 g (three case–control studies and one cohort study) and birth weight >4,000 g (four case–control studies and one cohort study). Parental age (<25 or >35 years) was also not associated with the risk of soft tissue tumors based on three cohort studies for maternal age <25 years and one case–control and one cohort study for parents >35 years. Head circumference (<33 or >38 cm) (74) and gestational diabetes (86) were not associated with the risk of soft tissue tumors, each based on one case–control study.
Parental smoking was not associated with the risk of soft tissue tumors based on estimates from three case–control studies and one cohort study. Paternal occupational exposure to pesticides showed an elevated risk of soft tissue tumors (ES 1.50), but with wide confidence interval, based on estimates from two cohort studies. Children exposed to traffic density likewise showed an elevated risk of soft tissue tumor (RR 1.40), albeit based on only one cohort study (128) (Figures 2–4; Table 3; Supplementary Material, page 35).
Discussion
Our systematic review and meta-analysis included 75 articles published between 1988 and 2024 on children diagnosed with retinoblastoma, hepatoblastoma, bone tumors, germ cell tumors, and soft tissue tumors. Among birth characteristics, low birth weight (<2,500 g) was associated with an increased risk of retinoblastoma and hepatoblastoma. C-section, ART, SGA, and older parental age (>35 years) were also associated with the risk of hepatoblastoma. For bone tumors, only high birth weight (>4,000 g) showed a suggestive association. No associations were observed between the risk factors evaluated and the risk of germ cell tumors. Paternal occupational exposure to pesticides was associated with an increased risk of retinoblastoma. Paternal smoking during preconception/pregnancy was associated with an increased risk of hepatoblastoma. Although only a few risk factors were significantly associated with specific childhood cancer types, several others showed elevated ES with wide confidence intervals, indicating non-significant elevations.
The borderline association observed between low birth weight (<2,500 g) and the risk of retinoblastoma may be influenced by other factors, including maternal smoking and alcohol consumption, maternal health conditions, and nutritional status, such as insufficient iron and folic acid supplementation (129–133). However, the pooled estimate for retinoblastoma (ES 1.27, 95% CI 0.99–1.63) was higher than that reported in a recent systematic review and meta-analysis by Rashti et al. in 2025 (134). The authors reported a pooled estimate of ES 0.95 (CI 0.68–1.32) based on one traditional case–control study, one registry-based case–control study, and one pooled analysis which they collectively referred to as “three case–control studies.” In our systematic review and meta-analysis, we included two additional studies (Heck et al., 2012, conducted in California, and Heck et al., 2020, conducted in China—Taiwan) (58, 95) and excluded the pooled analysis from the USA (135), as the California data were updated with 42 cases of retinoblastoma and published separately. Our results showing no association between ART and retinoblastoma align with the systematic review and meta-analysis by Song et al. in 2025 (136).
Some pesticides are genotoxic and can disrupt cell signaling, apoptosis, and cellular proliferation (137). Parental exposure to pesticides may increase the risk of childhood cancer through several windows of susceptibility: preconception, pregnancy, or the postnatal period. Preconception exposures may induce mutations or epigenetic alterations, such as changes in genomic imprinting or DNA methylation, in sperm. Exposures during pregnancy or postnatally may lead to somatic mutations or disrupt hormonal and immunologic function (138–140). In our analysis, paternal occupational exposure to pesticides was associated with an increased risk of retinoblastoma and showed a similarly elevated estimate for soft tissue tumors (ES 1.50), although with a wide confidence interval. Previous systematic reviews and meta-analyses on pesticides and childhood cancer have primarily focused on leukemia and brain tumors, where positive associations have been consistently reported (51, 141–147).
Similar to retinoblastoma, the threefold association observed between low birth weight (<2,500 g) and hepatoblastoma risk may have been influenced by the factors discussed above and other confounders. SGA is strongly correlated with low birth weight (148). In the present systematic review and meta-analysis, its association with hepatoblastoma was of lower magnitude (1.76-fold) compared to low birth weight (<2,500 g). Our findings showing a threefold increased risk of hepatoblastoma among children with low birth weight are consistent with previous epidemiological studies and meta-analyses identifying low birth weight as one of the strongest established risk factors for hepatoblastoma (44, 135). Several biological mechanisms have been proposed to explain this association. Low birth weight and prematurity are frequently associated with neonatal intensive care interventions, including oxygen therapy, with parental nutrition, and with exposure to certain medications. These factors may contribute to oxidative stress, DNA damage, or altered liver development during critical periods of growth (149). None of those proposed mechanisms is widely accepted though.
At least over 8 million children (live births) worldwide are conceived through ART (150), and 2% of children conceived in the USA are through ART (151). Among the childhood cancers reported in this present systematic review and meta-analysis, ART and older parental age (>35) were associated with increased risks of hepatoblastoma. Older parental age may contribute to hepatoblastoma risk through several biologically plausible pathways. Age-related germline mutations, particularly in fathers, increase with each additional year of spermatogonial cell division and may elevate the likelihood of de novo variants associated with embryonal tumors (152). Advanced maternal or paternal age has also been linked to epigenetic alterations, including imprinting errors relevant to hepatoblastoma’s association with imprinting disorders such as Beckwith–Wiedemann syndrome (153). Declining oocyte quality and increased chromosomal instability in older mothers may further contribute to developmental susceptibility (154). Additionally, oxidative stress and mitochondrial dysfunction in aging gametes may impair early embryonic liver development (155). While these mechanisms are plausible, they remain speculative, and further mechanistic studies are needed to clarify their relevance.
Children born through C-sections may be at a higher risk of developing malignancies (156). We observed an association between C-section and the risk of hepatoblastoma. Several hypotheses have been proposed to explain the potential link between C-section and childhood cancer. One of the hypotheses suggests that the lack of exposure to the maternal vaginal canal may limit the transfer of the maternal vaginal microbiome to the neonatal gut during a critical window of development, potentially influencing health outcomes later in life (157, 158). Moreover, neonates delivered by C-section do not experience the physiological stress of vaginal delivery, which normally activates the hypothalamic–pituitary–adrenal axis and primes the immune system for future function. This absence of early stress may create a permissive environment for malignancies to develop later in life (89, 159) Previous systematic reviews and meta-analyses have reported associations between C-sections and childhood leukemia (145, 160), Wilms tumor (52, 161), and neuroblastoma (162). Although the direction of association was generally consistent, given the observed heterogeneity across studies, interpreting the findings should be done with appropriate caution. In our study, evidence suggests that paternal smoking during preconception/pregnancy is positively associated with hepatoblastoma, with consistent findings in studies conducted in the UK and US. However, similar associations have previously been reported only in systematic reviews and meta-analyses of other types of childhood cancer (51, 163, 164).
Our findings of an association between high birth weight and an increased risk of bone tumors in children is consistent with previous systematic reviews and meta-analyses (165, 166). The two studies contributing to our pooled estimate were both conducted in Europe (74, 101). However, substantial heterogeneity was observed between studies, which may reflect differences in study populations, methodological approaches, exposure classification, adjustment for confounding factors, and sample sizes. Therefore, the pooled estimate should be interpreted with caution. Pooled estimates for older parental age (>35 years) did not indicate an increased risk of bone tumors, soft tissue tumors, or germ cell tumors. In contrast, Domingues et al. (2022) reported a borderline association between maternal age and childhood germ cell tumors (ES 1.06, 95% CI 1.00–1.12) per 5-year increase. Their estimate is broadly comparable to ours (ES 1.24, 95% CI 0.93–1.66), with differences likely reflecting variations in study inclusion and exclusion criteria (48).
Whether findings rely more on cohort or on case–control studies in the primary meta-analyses has important implications for interpretation. These study designs differ fundamentally in their susceptibility to bias (e.g., recall and selection bias in case–control studies versus loss to follow-up in cohort studies). As a result, combining them may increase statistical heterogeneity. Although the use of a random-effects model partially accounts for between-study variability, residual heterogeneity related to study design remains. Our stratified analyses by study design provide additional context, allowing an assessment of the consistency and robustness of the findings across the two approaches. Where estimates were broadly consistent, this supports the overall validity of the pooled results; however, where differences were observed, findings should be interpreted with caution.
Strengths and limitations
This systematic review and meta-analysis has several limitations. First, the number of eligible studies was limited, and for many risk factors and cancer types the available evidence was sparse. Most existing systematic reviews and meta-analyses in childhood cancer with adequate study numbers focus primarily on childhood leukemia and brain tumors, leaving other cancer types insufficiently studied. Second, the pooled effect sizes were derived from a combination of case–control and cohort studies, each of which carries inherent sources of bias that cannot be fully ruled out despite methodological precautions. Moreover, some extracted risk estimates were not adjusted for confounding factors, thereby reducing the internal validity of those findings. Finally, the geographical distribution of the included studies was heavily skewed, with most conducted in North America and Europe and only a small number originating from Asia, Oceania, and Latin America. Notably, no eligible studies were identified from Africa, where the exposure levels for several environmental risk factors are comparatively higher. Since the included studies were mainly conducted in high-income countries, the observed associations likely reflect exposure patterns, healthcare contexts, and underlying population characteristics typical of these settings. As a result, generalizing the findings to LMICs’ settings may be inappropriate, given potential differences in exposure prevalence, healthcare access, diagnostic practices, and data availability.
Subgroup and sensitivity analyses by tumor sub-types, publication periods, years of diagnosis, and geographical regions were not feasible because the original studies did not report sufficiently often results according to these specific subgroup classifications (e.g., unilateral vs. bilateral retinoblastoma, gonadal vs. extragonadal germ cell tumors). The overall limited number of available studies substantially restricted the possibility of conducting meaningful stratified analyses by publication periods, years of diagnosis, and geographical regions. These limitations should be considered when interpreting the findings. Our study also has several notable strengths. These include a rigorously designed and well-structured search strategy as well as the separation of case–control and cohort/registry-based studies in the meta-analysis to account for study design differences. Additionally, we stratified the analyses by the timing and source of exposure, distinguishing between paternal, maternal, and childhood exposures, as well as preconception, prenatal, and postnatal exposure windows. This approach enhances the precision and clarity of our findings.
Conclusion
This review and meta-analysis suggests only a few modifiable risk factors for rare childhood cancers, including paternal smoking for hepatoblastoma and paternal occupational exposure to pesticides for retinoblastoma during preconception/pregnancy. Wide CIs for pooled ES show that the database for evidence synthesis is limited and more and larger studies for rare childhood cancers are needed, with international collaboration to increase sample sizes, which is essential for informing strategies for the primary prevention of childhood cancer.
Funding Statement
The author(s) declared that financial support was received for this work and/or its publication. The study was funded by a grant from the French National Cancer Institute (INCa:15670; PEDIAC consortium). The funder had no role in the design of the study; extraction, management, analysis, and interpretation of the data; preparation, review, or approval of the manuscript; and decision to submit the manuscript for publication.
Footnotes
Edited by: Juan Manuel Mejia-Arangure, Universidad Nacional Autonoma de Mexico, Mexico
Reviewed by: Antonio Sandoval-Cabrera, Universidad Autónoma del Estado de México, Mexico
Danielle Awounou, Institut National de la Santé et de la Recherche Médicale (INSERM), France
Author contributions
FO: Investigation, Methodology, Software, Validation, Writing – review & editing. RD: Investigation, Methodology, Software, Validation, Writing – review & editing. AO: Methodology, Supervision, Validation, Writing – review & editing. LB: Writing – review & editing. JS: Funding acquisition, Methodology, Resources, Supervision, Writing – review & editing.
Conflict of interest
The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
The handling editor JM-A declared a past co-authorship with the author JS.
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Where authors are identified as personnel of the International Agency for Research on Cancer/World Health Organization, the authors alone are responsible for the views expressed in this article, and they do not necessarily represent the decisions, policy, or views of the International Agency for Research on Cancer/World Health Organization.
Supplementary material
The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fonc.2026.1797553/full#supplementary-material
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