Key Points
Question
Given that cancer incidence is higher among males than among females globally, to what extent do modifiable lifestyle behaviors and health conditions contribute to this disparity by sex across diverse populations?
Findings
In this multicohort study of 589 766 adults in China and the UK, 11 measured factors jointly accounted for 84% of the male-female gap in non−sex-specific cancer incidence (183 cases per 100 000 person-years) in the Chinese population but only 26% (52 cases per 100 000 person-years) in the UK population.
Meaning
These findings suggest that the contribution of modifiable lifestyle behaviors and health conditions to the male-female cancer gap varies across populations, underscoring the need for population-specific prevention.
Abstract
Importance
Cancer risk is higher in males than females globally. Whether this sex disparity reflects a biological inevitability or is potentially modifiable by lifestyle behaviors and health conditions across diverse populations remains unclear.
Objective
To determine the contribution of lifestyle factors and health conditions to sex disparities in cancer incidence across populations.
Design, Setting, and Participants
This cohort study conducted an individual-level analysis of 3 population-based prospective cohorts in China (Shanghai Men’s Health Study and Shanghai Women’s Health Study) and the UK (UK Biobank) of adults aged 40 to 74 years at baseline with no prior cancer. Baseline data were collected from 1997 to 2010, with follow-up through 2021. Data were analyzed from September 2025 to June 2026.
Exposures
Eleven risk factors covering behaviors (smoking, heavy alcohol drinking, physical inactivity), diet (low intakes of vegetable and fruit, high intakes of red meat and processed meat), and health conditions (cholelithiasis, chronic liver diseases, diabetes, obesity).
Main Outcomes and Measures
Incidence of 34 non−sex-specific cancer end points. Attributable rate differences (ARDs, cases per 100 000 person-years) and attributable proportion (AP, %) quantified the number and percentage of the male-female incidence rate gap attributable to the exposures.
Results
Among a total of 589 766 participants (mean [SD] age, 56.1 [8.5] years; 315 813 [53.5%] females), 70 300 non−sex-specific cancer cases were documented. In the Chinese population (134 742 participants [54.4% female]), the joint ARD across the 11 risk factors was 182.52 (95% CI, 162.46-202.26) cases per 100 000 person-years, accounting for 84.44% of the male-female incidence rate difference. Smoking (ARD, 111.87 [95% CI, 95.38-128.00]; AP, 51.75%) and heavy alcohol drinking (ARD, 32.64 [95% CI, 24.61-40.43]; AP, 15.10%) were leading contributors. In the UK population (455 024 participants [53.3% female]), the joint ARD was 52.31 (95% CI, 35.63-70.22) cases per 100 000 person-years, accounting for 26.21% of the sex disparity. Obesity (ARD, 15.34 [95% CI, 6.06-24.08]; AP, 7.68%) and smoking (ARD, 12.49 [95% CI, 1.82-24.39]; AP, 6.26%) were leading individual contributors.
Conclusions and Relevance
The findings of this cohort study suggest that modifiable lifestyle factors and health conditions accounted for most of the male-female cancer incidence gap in the Chinese population but only a small fraction in the UK population. Reducing cancer sex disparities may require prevention strategies tailored to population contexts.
This cohort study evaluates the contribution of lifestyle factors and health conditions to sex disparities in cancer incidence across populations.
Introduction
Cancer incidence is consistently higher among males than females for most non−sex-specific sites globally. Although such male predominance is well documented, the underlying drivers remain debated. Biological determinants (eg, genetic makeup, sex hormones, immune responses) contribute to differential susceptibility, while modifiable lifestyle behaviors and health conditions, shaped by societal and cultural norms, may also play a role. Distinguishing their relative contributions is crucial for precision public health interventions.
Despite the importance of this issue, quantitative evidence on how specific risk factors contribute to the male-female cancer gap remains limited. Most previous reports relied on aggregate registry data lacking individual-level exposure, and the few prospective cohort studies addressing this question were restricted to a single population or did not explicitly quantify the contribution of specific risk factors. To our knowledge, no study has systematically quantified and directly compared the contributions of multiple lifestyle factors and health conditions to sex disparities in cancer incidence across diverse populations. The Chinese and UK populations provide an informative contrast in both sociocultural context and risk-factor distribution. Smoking and heavy alcohol drinking are strongly concentrated among males in the Chinese population but are more similar between the sexes in the UK population. Obesity and related metabolic conditions also differ between the settings. These contrasting exposure patterns allow us to assess whether the contribution of modifiable risk factors to cancer disparities by sex varies by population context.
To address this gap, we analyzed individual-level data from more than half a million participants in 3 prospective cohorts in China and the UK, mapping exposure and outcomes to common analytic definitions where possible and applying a unified analytic framework across populations. We quantified sex disparities across 34 non−sex-specific cancer end points and the extent to which 11 lifestyle factors and health conditions contributed to these disparities in diverse population contexts. We hypothesized that modifiable risk factors would account for a larger proportion of the disparity in populations where socially and culturally patterned behaviors, such as smoking and alcohol consumption, differ markedly between males and females. These findings may inform population- and sex-specific cancer prevention.
Methods
The institutional review board of the Shanghai Cancer Institute approved both Chinese studies and the North West Multi-center Research Ethics Committee approved the UK Biobank study. All participants provided written informed consent. Additionally, this work was conducted under the UK Biobank Application No. 833162 and approved by the Renji Hospital Ethics Committee of Shanghai Jiao Tong University School of Medicine (KY2026-016-B). We followed the Strengthening the Reporting of Observational Studies in Epidemiology (STROBE) reporting guideline.
Study Population
The Shanghai Women’s Health Study (SWHS; 74 940 female residents aged 40-70 years [baseline 1997-2000]) and the Shanghai Men’s Health Study (SMHS; 61 469 male residents aged 40-74 years [baseline 2002-2006]) are population-based prospective cohorts in Shanghai, China. These age ranges reflect the original cohort designs and the concentration of cancer incidence at age 40 years and older. Trained staff conducted in-person baseline interviews to collect information on demographic characteristics, medical and family history, diet, physical activity, and other lifestyle factors. Incident cancer cases and deaths were ascertained through annual linkage to the Shanghai Cancer Registry and Vital Statistics Registry, supplemented by active follow-up. Cancer incidence data were censored on December 31, 2020. Given their shared source population and similar designs, SWHS and SMHS were combined to represent the urban population in Shanghai, China.
The UK Biobank recruited 502 000 participants aged 40 to 70 years from 22 assessment centers across the UK during 2006 to 2010. Touchscreen questionnaires captured sociodemographic factors, lifestyle, family history, and medical history. Cancer diagnoses and deaths were ascertained via linkage to national cancer and death registries. Censoring dates for cancer diagnosis were December 31, 2020 (England), November 30, 2021 (Scotland), and December 31, 2016 (Wales).
Outcome Ascertainment
Cancer outcomes were coded using the International Classification of Diseases, Ninth Revision (ICD-9) for the Chinese cohorts and the ICD-10 for the UK cohort. The study outcome included all non−sex-specific primary cancers (ICD-9 codes 140-195 and 200-208; ICD-10 codes C00-C75 and C81-C96), excluding breast and genital-organ cancers (ICD-9 codes, 174-187; ICD-10 codes, C50-C63) because they affect a single sex either exclusively (genital organs) or almost exclusively (breast), precluding a male-female comparison. End point definitions are detailed in eTable 1 in Supplement 1. We focused on non−sex-specific cancers combined, 4 systems (respiratory, digestive, urinary, hematological), and individual sites with ≥5 incident cases in either sex. Follow-up time was calculated from study enrollment to cancer diagnosis, death, loss to follow-up, or administrative censoring, whichever came first.
Participants with prior cancer at baseline were excluded. Sex-specific cancers during follow-up were not study end points, but affected participants continued contributing person-time. For the combined end point, follow-up was censored at the first non−sex-specific cancer.
Selection of Risk Factors
We selected 11 lifestyle factors and health conditions based on the International Agency for Research on Cancer monographs, the World Cancer Research Fund continuous updating reports, and recent meta-analyses (detailed in eTable 2 in Supplement 1): 3 behavioral factors (cigarette smoking, heavy alcohol drinking, physical inactivity), 4 dietary factors (low intake of vegetable and fruit, high intake of red meat and processed meat), and 4 health conditions (cholelithiasis, chronic liver diseases, diabetes, obesity). Owing to questionnaire heterogeneity across cohorts, exposures with established clinical thresholds were defined accordingly, whereas dietary and physical activity factors without universal cut-points were categorized using population- and sex-specific quartiles (eTable 3 in Supplement 1). Only baseline exposures were used because repeated assessments were unavailable for the entire study population.
Statistical Analysis
Baseline characteristics were summarized by sex within each population and between the 2 populations. Group differences were quantified using standardized differences.
Age-standardized incidence rate (ASIR) per 100 000 person-years (PYs) was calculated for ages 40 to 84 years using the Segi-Doll world standard population. The 95% CIs were calculated based on a gamma distribution to accommodate the small-event-count setting.
Sex disparities were quantified on relative and absolute scales. The male to female incidence rate ratio (IRR) was estimated from a Poisson regression model with log(PYs) as offset, adjusted for age (natural spline, 3 degrees of freedom) and birth cohort (10-year groups). The absolute sex gap was quantified as the difference between the male and female ASIRs, and the 95% CIs were derived from a normal approximation. Age-stratified analyses (5-year strata) were conducted for non−sex-specific cancers combined.
Five-year population attributable fractions (PAFs) for each end point were estimated from sex-specific Cox proportional hazards models including all site-specific risk factors and adjusted for age, birth cohort, cohort-specific categories of education and income, and country within the UK Biobank. Joint PAFs were computed by setting all risk factors to the low-risk reference. Participants with missing covariates were excluded from each model (<1% for all variables except physical activity in UK Biobank [21.3%]; eTable 5 in Supplement 1). “Prefer not to answer” responses for education and income were retained as separate categories.
To integrate rate-based magnitude with risk-factor attribution, we defined the attributable rate difference (ARD) for each factor as ASIRmales × PAFmales − ASIRfemales × PAFfemales, representing the male-female incidence rate difference (per 100 000 PYs) attributable to that factor (eFigure 1 in Supplement 1). This approach is analogous to established decomposition methods used in prior research. Joint ARDs were computed analogously, since single-factor ARDs under a counterfactual framework are not additive. The 95% CIs were obtained from 1000 nonparametric bootstrap replicates (percentile method). The proportion of the male-female rate difference attributable to the exposures (attributable proportion, AP; %) was calculated as ARD / (ASIRmales − ASIRfemales) × 100% (eFigure 1 in Supplement 1).
Three sensitivity analyses were conducted: (1) 10-year PAFs; (2) multiple imputation for physical activity data in the UK Biobank; and (3) Fine-Gray subdistribution hazards models with death as competing event. Mortality from non−sex-specific cancers was analyzed as a secondary outcome using the same framework applied to incidence. Full methodologic details are provided in the eMethods in Supplement 1.
Analyses were performed in R, version 4.5.1 (R Project for Statistical Computing). Two-sided P < .05 was considered statistically significant. Data were analyzed from September 2025 to June 2026.
Results
After excluding participants with prior cancer and mismatched sex, 589 766 participants were included (eFigure 2 in Supplement 1): 134 742 from the 2 Shanghai cohorts (45.6% males) and 455 024 from the UK Biobank (46.7% males). Demographic and risk factor distributions are shown by sex in Table 1, and by study population in eTable 4 in Supplement 1. Because the primary comparisons were within each population, between-population differences were treated as contextual characteristics.
Table 1. Demographic Characteristics and Cancer Risk Factor Distributions by Sex Within Each Populationa.
| Characteristic | Sample population, No. (%) | |||||
|---|---|---|---|---|---|---|
| China | UK | |||||
| Male (n = 61 433) | Female (n = 73 309) | SMD | Male (n = 212 520) | Female (n = 242 504) | SMD | |
| Age at study enrollment, median (IQR), y | 53.1 (47.4-63.5) | 50.3 (44.4-60.9) | 0.303 | 58.1 (50.2-63.7) | 57.6 (50.1-63.1) | 0.040 |
| Cancer diagnosis | 7173 (11.7) | 6954 (9.5) | 0.071 | 31 354 (14.8) | 24 819 (10.2) | 0.025 |
| Incidence rate (95% CI)b | 783.93 (765.78-802.07) | 465.09 (454.16-476.02) | NA | 1157.62 (1144.81-1170.44) | 774.22 (764.59-783.86) | NA |
| Age at cancer diagnosis, median (IQR), y | 58.9 (50.4-68.5) | 56.0 (47.2-64.2) | 0.371 | 62.5 (57.5-66.2) | 61.7 (56.0-65.6) | 0.134 |
| Birth cohort | ||||||
| ≤1940 | 14 570 (23.7) | 21 646 (29.5) | 0.535 | 7688 (3.6) | 7612 (3.1) | 0.054 |
| 1941-1950 | 13 377 (21.8) | 19 304 (26.3) | 91 435 (43.0) | 99 767 (41.1) | ||
| 1951-1960 | 26 166 (42.6) | 32 346 (44.1) | 67 160 (31.6) | 81 859 (33.8) | ||
| ≥1961 | 7320 (11.9) | 13 (0.0) | 46 237 (21.8) | 53 266 (22.0) | ||
| Education levelc | ||||||
| Middle school or above (China); any qualification (UK) | 56 489 (92.0) | 57 627 (78.6) | 0.462 | 174 435 (82.1) | 200 097 (82.5) | 0.013 |
| Elementary school or less (China); no formal qualification (UK) | 4080 (6.6) | 15 669 (21.4) | 35 665 (16.8) | 39 880 (16.4) | ||
| Prefer not to answer | 864 (1.4) | 13 (0.0) | 2420 (1.1) | 2527 (1.0) | ||
| Income leveld | ||||||
| At or above cohort- and sex-specific threshold | 53 584 (87.2) | 61 491 (83.9) | 0.114 | 149 659 (70.4) | 150 472 (62.0) | 0.202 |
| Below cohort- and sex-specific threshold | 7721 (12.6) | 11 802 (16.1) | 37 985 (17.9) | 48 014 (19.8) | ||
| Prefer not to answer | 128 (0.2) | 16 (0.0) | 24 876 (11.7) | 44 018 (18.2) | ||
| Ever cigarette smokere | 42 765 (69.6) | 2042 (2.8) | 1.935 | 107 036 (50.7) | 95 724 (39.7) | 0.222 |
| Heavy alcohol drinkere,f | 16 336 (26.6) | 663 (0.9) | 0.804 | 53 503 (25.2) | 38 628 (15.9) | 0.231 |
| Obesityg | 23 232 (37.8) | 21 470 (29.3) | 0.181 | 73 320 (34.5) | 92 205 (38.0) | 0.073 |
| Physical inactivityh | 15 304 (24.9) | 18 325 (25.0) | 0.002 | 43 692 (25.0) | 45 692 (24.9) | 0.001 |
| Not reported | 0 | 0 | 37 592 (17.7) | 59 182 (24.4) | ||
| High intake of processed meate,i | 1349 (2.2) | 12 484 (17.0) | 0.520 | 91 892 (43.2) | 49 990 (20.6) | 0.500 |
| High intake of red meatj | 15 358 (25.0) | 18 328 (25.0) | <0.001 | 62 400 (29.4) | 60 809 (25.1) | 0.096 |
| Low intake of vegetablesk | 15 358 (25.0) | 18 327 (25.0) | <0.001 | 44 219 (20.8) | 32 323 (13.3) | 0.200 |
| Low intake of fruitsk | 15 358 (25.0) | 18 327 (25.0) | <0.001 | 19 637 (9.2) | 43 542 (18.0) | 0.256 |
| Diabetese | 3861 (6.3) | 3167 (4.3) | 0.088 | 15 472 (7.3) | 9547 (3.9) | 0.146 |
| Chronic liver diseases | 4714 (7.7) | 1890 (2.6) | 0.233 | 2042 (1.0) | 1498 (0.6) | 0.039 |
| Cholelithiasise | 4621 (7.5) | 8180 (11.2) | 0.125 | 3548 (1.7) | 10 931 (4.5) | 0.165 |
Abbreviations: BMI, body mass index (calculated as weight in kilograms divided by height in meters squared); MET, metabolic equivalent of task; NA, not applicable; SMD, standardized mean difference; WC, waist circumference.
The total percentage may not equal 100% due to rounding.
No. of events per 100 000 person-years.
Education definitions were population specific: middle school or above vs elementary school or less in the Chinese population, and any formal qualification vs no formal qualification in the UK population. These categories reflect differences in the original questionnaires and are not directly comparable between populations.
Income definitions were cohort- and sex-specific: annual family income of <¥10 000 (US$1200) vs ≥¥10 000 for Chinese females; personal income of <¥500 ($60)/mo vs ≥¥500/mo for Chinese males; and annual average household income before tax of <£18 000 ($32 000) vs ≥£18 000 for the UK population. US dollar amounts are approximations and were converted using mean annual exchange rates during each cohort’s baseline period and are not adjusted for purchasing power parity. These conversions are provided for reference only and do not imply that these thresholds represent a common poverty standard or an equivalent position in the income distribution. The different income definitions and thresholds were defined in each cohort’s own baseline questionnaire and are not directly comparable across populations or between males and females in the Chinese cohorts.
Variables with missing values (proportion <1%). Details are presented in eTable 5 in Supplement 1. Proportions were calculated based on participants with nonmissing values.
Chinese population: alcohol intake frequency ≥7 times per week; UK population: alcohol intake frequency: daily or almost daily.
Chinese population: BMI ≥28; WC ≥83 cm (females) or 88 cm (males); UK population: BMI≥30 kg/m2; WC≥88 cm (females) or 102 cm (males).
Level of total physical activity (MET-h/week for Chinese population and MET-min/week for UK population)<the 25th percentile. Proportions were calculated based on participants with nonmissing values.
Frequency of processed meat intake >2 times (Chinese population) or ≥2 times (UK population) per week.
Intake ≥75th percentile.
Intake <25th percentile.
Sex Disparities in Cancer Incidence
During follow-up, 70 300 incident non−sex-specific cancer cases were documented. ASIRs are shown in eFigure 3 in Supplement 1. The overall male to female IRR was higher in the Chinese population (1.66; 95% CI, 1.60-1.72) than in the UK population (1.49; 95% CI, 1.46-1.51) (Table 2). On the absolute scale, the differences in ASIRs were 216.15 (95% CI, 197.37-234.93) and 199.62 (95% CI, 184.92-214.32) cases per 100 000 PYs (Table 2). The male-female gap emerged at an earlier age in the Chinese population than in the UK population (eResults and eFigures 4 and 5 in Supplement 1). Mortality was examined as a secondary and descriptive outcome and the results are presented in the eResults, eFigures 5 to 8, and eTables 7 and 9 in Supplement 1.
Table 2. Male to Female Incidence Rate Ratios (IRRs) and Differences in Age-Standardized Incidence Rates (ASIRs) by Cancer Site.
| Cancer site | Chinese population | UK population | ||
|---|---|---|---|---|
| IRR (95% CI) | Difference in ASIRs (95% CI) | IRR (95% CI) | Difference in ASIRs (95% CI) | |
| Non−sex-specific cancers combined | 1.66 (1.60 to 1.72) | 216.15 (197.37 to 234.93) | 1.49 (1.46 to 1.51) | 199.62 (184.92 to 214.32) |
| Respiratory system | 1.80 (1.68 to 1.92) | 71.99 (62.39 to 81.60) | 1.35 (1.28 to 1.43) | 13.13 (9.75 to 16.51) |
| Nasal cavities, middle ear and accessory sinuses | 2.82 (1.49 to 5.35) | 2.44 (0.18 to 4.70) | 1.34 (0.82 to 2.18) | 1.05 (−0.04 to 2.13) |
| Larynx | 13.98 (7.45 to 26.22) | 9.12 (5.90 to 12.33) | 11.82 (7.47 to 18.71) | 3.83 (3.15 to 4.51) |
| Lung | 1.71 (1.60 to 1.84) | 59.91 (51.23 to 68.58) | 1.26 (1.19 to 1.34) | 8.07 (4.96 to 11.19) |
| Thymus, heart, and mediastinum | 1.83 (1.03 to 3.25) | 0.65 (−0.49 to 1.80) | 1.10 (0.61 to 2.00) | 0.05 (−0.19 to 0.29) |
| Digestive system | 1.75 (1.66 to 1.83) | 111.71 (99.09 to 124.33) | 1.63 (1.57 to 1.69) | 50.00 (44.02 to 55.99) |
| Esophagus | 3.93 (3.02 to 5.12) | 12.42 (8.93 to 15.90) | 3.13 (2.75 to 3.55) | 11.67 (10.10 to 13.24) |
| Stomach | 2.29 (2.07 to 2.53) | 35.60 (28.58 to 42.62) | 2.35 (2.04 to 2.72) | 6.82 (5.19 to 8.46) |
| Small intestine | 1.13 (0.74 to 1.73) | 0.34 (−0.78 to 1.46) | 1.45 (1.16 to 1.82) | 1.69 (0.46 to 2.92) |
| Colon | 1.32 (1.21 to 1.44) | 11.36 (6.08 to 16.64) | 1.28 (1.21 to 1.36) | 7.66 (3.79 to 11.54) |
| Rectum | 1.66 (1.48 to 1.87) | 14.49 (9.50 to 19.48) | 1.91 (1.76 to 2.07) | 13.57 (10.65 to 16.49) |
| Liver | 2.83 (2.47 to 3.24) | 33.23 (27.84 to 38.63) | 2.46 (2.11 to 2.87) | 5.46 (4.30 to 6.63) |
| Gallbladder | 0.82 (0.66 to 1.02) | −2.70 (−4.86 to −0.54) | 1.09 (0.89 to 1.33) | 0.54 (−0.48 to 1.55) |
| Pancreas | 1.48 (1.28 to 1.71) | 7.85 (4.80 to 10.90) | 1.35 (1.22 to 1.49) | 4.02 (2.05 to 6.00) |
| Other and ill-defined digestive organs | 1.63 (0.80 to 3.33) | 0.21 (−0.32 to 0.73) | 0.98 (0.52 to 1.83) | −0.03 (−0.32 to 0.26) |
| Urinary system | 2.59 (2.28 to 2.93) | 32.30 (26.64 to 37.97) | 2.78 (2.58 to 3.00) | 27.91 (25.21 to 30.61) |
| Kidney | 1.91 (1.62 to 2.25) | 15.41 (11.30 to 19.52) | 2.27 (2.07 to 2.49) | 14.05 (11.79 to 16.32) |
| Bladder | 3.89 (3.18 to 4.75) | 16.94 (13.03 to 20.84) | 4.01 (3.53 to 4.56) | 14.41 (12.92 to 15.89) |
| Hematologic system | 1.43 (1.25 to 1.65) | 7.21 (3.17 to 11.24) | 1.51 (1.43 to 1.60) | 22.85 (18.25 to 27.45) |
| Non-Hodgkin lymphoma | 1.26 (1.04 to 1.52) | 2.74 (−0.11 to 5.60) | 1.47 (1.38 to 1.57) | 14.97 (11.38 to 18.56) |
| Hodgkin disease | 1.55 (0.50 to 4.84) | 0.11 (−0.28 to 0.50) | 1.40 (1.05 to 1.88) | 0.53 (−0.68 to 1.75) |
| Leukemia | 1.60 (1.22 to 2.10) | 2.54 (0.15 to 4.93) | 1.62 (1.38 to 1.90) | 2.55 (1.04 to 4.05) |
| Multiple myeloma | 1.82 (1.30 to 2.54) | 1.76 (0.26 to 3.26) | 1.62 (1.44 to 1.82) | 5.22 (3.07 to 7.38) |
| Other systems | ||||
| Oral cavity | 2.35 (1.89 to 2.94) | 9.22 (6.11 to 12.33) | 2.29 (2.03 to 2.58) | 12.17 (9.92 to 14.41) |
| Thyroid | 0.33 (0.27 to 0.40) | −19.82 (−24.20 to −15.43) | 0.45 (0.37 to 0.54) | −5.67 (−7.67 to −3.66) |
| Other endocrine glands and related structures | 1.17 (0.56 to 2.48) | 0.10 (−0.57 to 0.77) | 1.16 (0.61 to 2.19) | 0.41 (−0.38 to 1.19) |
| Melanoma | 0.78 (0.36 to 1.66) | −0.47 (−1.38 to 0.44) | 1.25 (1.16 to 1.33) | 0.40 (−4.38 to 5.19) |
| Nonmelanoma skin | 1.36 (1.03 to 1.80) | 2.07 (0.27 to 3.87) | 1.43 (1.40 to 1.46) | 80.84 (70.97 to 90.71) |
| Central nervous system | 0.84 (0.67 to 1.07) | −1.04 (−4.75 to 2.67) | 1.62 (1.42 to 1.85) | 5.77 (3.52 to 8.02) |
| Heart, mediastinum, and pleura | 1.80 (0.51 to 6.37) | 0.15 (−0.22 to 0.52) | 2.56 (0.89 to 7.36) | 0.49 (−0.25 to 1.22) |
| Retroperitoneum and peritoneum | 0.53 (0.25 to 1.14) | −0.55 (−1.39 to 0.30) | 0.20 (0.13 to 0.30) | −2.41 (−3.27 to −1.55) |
| Bone and articular cartilage | 1.01 (0.53 to 1.93) | 0.19 (−0.63 to 1.01) | 2.19 (1.27 to 3.76) | 0.95 (0.09 to 1.81) |
| Connective and other soft tissue | 1.39 (0.85 to 2.28) | −0.39 (−1.86 to 1.08) | 1.77 (1.39 to 2.25) | 1.30 (−0.27 to 2.87) |
Abbreviations: IRR, incidence rate ratio; ASIR, age-standardized incidence rate.
The IRR was estimated from a Poisson regression model adjusted for age and birth cohort.
Sex-Specific Population Attributable Fractions
The 5-year PAFs of 11 risk factors are summarized in Figure 1. In the Chinese population, smoking was the dominant individual factor in males, with PAFs of 21.67% for non−sex-specific cancers combined and 57.61% for lung cancer, vs 0.79% and 4.04% in females (Figure 1A). Heavy alcohol drinking had particularly high PAFs for cancers of esophagus, oral cavity, and stomach. Conversely, obesity had higher PAFs among Chinese females for some cancers (eg, liver, 19.98% vs 2.04%).
Figure 1. Heatmap of Sex-Specific 5-Year Population Attributable Fraction (PAF) for Cancer Incidence.

Bolded values indicate statistical significance (P < .05); blank cells are those in which the risk factor was not modeled for the cancer site; and “All” is non−sex-specific cancers combined.
In the UK population, the contribution of risk factors was more similar across sexes (Figure 1B). Although smoking prevalence was higher in males, the lung-cancer PAF for smoking was substantial in both sexes (75.51% in males, 66.63% in females). Obesity was prominent in UK females for gallbladder cancer (17.08% vs 6.11% in males) and thyroid cancer (12.56% vs 3.81%), contrasting with the Chinese pattern.
Risk Factor Contributions to the Male-Female Cancer Rate Gap
We translated PAFs into ARDs and APs, quantifying the number and proportion of the male-female incidence gap attributable to the modeled risk factors (Figures 2 and 3; eTable 8 in Supplement 1; conceptual schematic and worked example in eFigure 1 in Supplement 1). For non−sex-specific cancers combined, the joint ARD across the 11 risk factors was 182.52 (95% CI, 162.46-202.26) per 100 000 PYs in the Chinese population, accounting for 84.44% of the sex gap. In the UK population, the corresponding joint ARD and AP were 52.31 (95% CI, 35.63-70.22) and 26.21%. Because single-factor ARDs and APs are not additive, joint and single-factor estimates are presented separately (Figures 2 and 3). The ARD estimates are quantitative attributions under the assumptions of the underlying Cox models and do not represent definitive causal partitions.
Figure 2. Horizontal Bar Plot of the Joint Attributable Rate Differences (ARD) and Attributable Proportion (AP) for the Male-Female Cancer Incidence Gap.

ARD is defined as ASIRmale × PAFmale − ASIRfemale × PAFfemale and is interpretable as the number of cases per 100 000 PYs of the male-female incidence rate gap attributable to the modeled risk factors. AP is defined as ARD / (ASIRmale − ASIRfemale) and is interpretable as the proportion of the male-female incidence rate gap attributable to the modeled risk factors. A conceptual schematic and a worked example are provided in eFigure 1 in Supplement 1. The joint ARD and AP reflect the combined, jointly estimated contribution of all risk factors modeled for a given site. Bars extending to the right (positive ARD) indicate a contribution to higher rates in males, and bars extending to the left (negative ARD) indicate a contribution to higher rates in females. Error bars denote 95% CIs. An interval crossing zero indicates the estimate was not statistically significant at the α = .05 level. Because single-factor ARDs are not additive, joint ARDs are presented separately, whereas single-factor ARDs are shown in Figure 3. The specific set of risk factors combined to compute the joint ARD and AP for each cancer site is provided in eTable 2 in Supplement 1. ASIR indicates age-standardized incidence rate; PAF, population attributable fraction; PYs, person-years.
Figure 3. Circular Bar Plot of Single-Factor Attributable Rate Difference (ARD) for the Male-Female Incidence Gap.

ARD is defined as ASIRmale × PAFmale − ASIRfemale × PAFfemale, and is interpretable as the absolute number of cases per 100 000 person-years of the male-female incidence rate gap attributable to a given risk factor. Bars extending outwards (positive ARD) indicate that the factor contributes to higher rates in males. Bar height corresponds to the absolute magnitude of the ARD. Bars in gray denote ARDs whose 95% CIs crossed zero (ie, not statistically significant at the α = .05 level). Because single-factor ARDs are not additive, their combined (joint) contribution across all modeled factors is shown separately in Figure 2. A conceptual schematic and a worked example are provided in eFigure 1 in Supplement 1. ARDs are model-based attributions and do not represent definitive causal partitions. All indicates all the non−sex-specific cancers combined; ASIR, age-standardized incidence rate; PAF, population attributable fraction.
In the Chinese population, the male-female incidence gap was dominated by behavioral factors of large magnitude (Figure 3A; eTable 8 in Supplement 1). Cigarette smoking alone was associated with 51.75% of the sex gap (ARD, 111.87 [95% CI, 95.38-128.00]) and was the leading contributor to the male-female gap in lung, stomach, rectum, and liver cancers. Heavy alcohol drinking exhibited an ARD of 32.64 (95% CI, 24.61-40.43) cases per 100 000 PYs and AP of 15.10%, with contributions concentrated in lung, esophagus, and stomach cancers. Chronic liver diseases (overall ARD, 21.72 [95% CI, 17.68-26.24]; AP, 10.05%) and low fruit intake (overall ARD, 21.42 [95% CI, 11.53-31.42]; AP, 9.91%) were the next leading contributors. Metabolic factors, including obesity and diabetes, contributed minimally to the gap for non−sex-specific cancers combined.
In the UK population, the contributing factors were more heterogeneous and were dominated by metabolic rather than behavioral exposures (Figure 3B; eTable 8 in Supplement 1). For non−sex-specific cancers combined, obesity was the leading contributor (ARD, 15.34 [95% CI, 6.06-24.08]; AP, 7.68%), followed by smoking (ARD, 12.49 [95% CI, 1.82-24.39]; AP, 6.26%) and diabetes (ARD, 7.00 [95% CI, 3.39-10.56]; AP, 3.51%).
Sensitivity Analyses
Extending the PAF horizon from 5 to 10 years yielded estimates concordant with the primary analysis, in both direction and magnitude (eTable 8 in Supplement 1). Subdistribution-hazard estimates (Fine-Gray model, with death as competing event) were materially similar to cause-specific Cox estimates (eTable 10 in Supplement 1). Multiple imputation for total physical activity in the UK Biobank (21.3% missing; eTables 5 and 6 in Supplement 1) yielded PAFs nearly identical to the complete-case analysis (eTable 11 in Supplement 1). Details of the sensitivity analyses are provided in eResults in Supplement 1.
Discussion
In 2 populations with contrasting risk factor profiles, we found that both the magnitude and composition of modifiable contributions to cancer sex disparities were highly setting-dependent. In the Chinese population, the male-female gap was predominantly attributable to marked sex differences in lifestyle behaviors, particularly cigarette smoking and heavy alcohol drinking. In contrast, in the UK population, these factors accounted for a substantially smaller proportion of the sex gap, leaving much of the disparity unexplained by the measured factors.
Although male predominance in cancer is consistent globally, the magnitude varies across sites, regions, and time periods. Registry-based studies have inferred potential drivers for this variation. For example, Carioli et al attributed epithelial cancer mortality patterns to historical smoking and alcohol epidemics, while Edgren et al labeled 13 cancer sites as “enigmatic” for lacking obvious environmental explanations. Our study extends these observations by shifting from ecological inference to individual-level quantification, expressing each factor’s contribution as absolute rate difference and a proportion of the male-female rate gap. Our findings in the UK population align with other Western cohorts. The US National Institutes of Health−American Association of Retired Persons study, using Peters-Belson decomposition (analogous to our ARD framework), found that smoking, alcohol, anthropometrics, diet, medication use, and medical history accounted for only a modest proportion (11.2%-49.4%) of the male-female incidence gap at 7 cancer sites and none at 12 sites. Surveillance, Epidemiology, and End Results program (US National Cancer Institute) analyses across 5 US racial and ethnic groups likewise showed largely stable male-to-female incidence rate ratios despite substantial differences in smoking and obesity prevalence, suggesting that lifestyle variation alone is insufficient to close the sex gap in Western populations. Our Chinese data indicate that this modest contribution is not universal. Where lifestyle patterns differ markedly between males and females, a substantial portion of the sex disparity in cancer is attributable to modifiable behaviors and therefore potentially preventable.
This context-dependent dichotomy is particularly evident in alcohol-related carcinogenesis. In East Asian populations, aldehyde dehydrogenase 2 (ALDH2) deficiency is common and limits acetaldehyde detoxification, amplifying cancer risk, while sociocultural norms are associated with much lower alcohol consumption among females. Therefore, alcohol exposure and its interaction with ALDH2 deficiency is concentrated predominantly in males. Targeted alcohol control among males may be a high-yield strategy for reducing sex disparities in alcohol-related cancers.
Metabolic dysregulation also contributed heterogeneously. In the UK population, diabetes contributed to higher incidence of liver and pancreatic cancers in males, highlighting the potential role of glycemic control. Conversely, obesity PAFs for gallbladder and thyroid cancers was concentrated in Chinese males but higher among UK females. This divergence indicates that obesity-attributable patterns are not uniform across populations. Adiposity promotes tumorigenesis through competing mechanisms, including insulin resistance, chronic inflammation, and sex hormone metabolism. Hormone-mediated pathways may predominate in the UK population, whereas inflammatory pathways linked to visceral adiposity, to which East Asian males are more predisposed, may dominate in the Chinese population. These hypotheses warrant investigation using body-composition and biomarker data.
Chronic liver disease contributed substantially to liver-cancer sex disparity in both populations, likely through distinct causes. Hepatitis B virus−related hepatitis and cirrhosis likely predominate in the Chinese population, whereas metabolic dysfunction-associated steatotic liver disease may be more prominent in the UK population, consistent with the greater contributions of obesity and diabetes to liver cancer that we observed.
Limitations
First, as an observational study, residual confounding and reverse causation cannot be ruled out. Because the SWHS and SMHS enrolled participants during slightly different periods (1997-2000 vs 2002-2006), sex is structurally confounded with cohort and calendar time in the Chinese analysis. Given rapid lifestyle transitions in China during this time, residual confounding by calendar time may persist despite adjustment for age and birth cohort. Income adjustment was crude and based on measures that were noncomparable across populations and internally inconsistent between the 2 Chinese cohorts. Education definitions also differed across populations. Although these variables were used only as covariates in sex- and population-specific models, they may have resulted in residual or differential socioeconomic confounding. Second, risk factors were assessed only at baseline to maintain data harmonization, and subsequent changes were not captured. Together with self-reporting, this may have introduced exposure misclassification. Third, we lacked data on occupational exposures, ambient air pollution, and specific infectious agents (eg, Helicobacter pylori, Epstein-Barr virus), precluding direct assessment of their contributions. These factors may be correlated with measured behaviors, and the estimated ARDs for behavioral factors may partially capture their effects. Fourth, dietary and physical activity factors were categorized using population- and sex-specific quartiles and therefore reflect relative rather than absolute exposure. Fifth, screening-coverage differences between the UK and China may have influenced site-specific incidence and ARDs. Sixth, all cohorts enrolled participants aged 40 to 74 years at baseline. Although follow-up extended into older ages, the oldest groups were underrepresented and early-onset cancers (age <40 years) were not captured. Because both the magnitude of the male-female gap and the contribution of specific factors may differ at the extremes of age, our estimates may not generalize to these groups and warrant investigation in cohorts spanning a wider age range. Finally, generalizability is limited because the Shanghai cohorts represent an urban Chinese population, whereas the UK Biobank is subject to a well-documented healthy-volunteer selection bias and is predominantly of White European ancestry. Race and ethnicity were unavailable in the Chinese cohorts, so within-population ethnic heterogeneity could not be examined. Therefore, comparisons across racial and ethnic populations should be interpreted with caution.
Conclusions
In this cohort study, contributions of lifestyle behaviors and health conditions to cancer sex disparities were not uniform across populations. In the Chinese population, a potential priority for helping address the cancer disparity by sex could be in targeting behavioral interventions, specifically tobacco and alcohol control among males. In the UK population, the measured risk factors accounted for only a modest proportion of the male-female rate gap, underscoring the need to investigate unmeasured occupational and environmental exposures, as well as intrinsic biological determinants. Recognizing that biological sex and sociocultural gender contribute differently to cancer across populations is essential for global cancer equity and sex-specific precision prevention strategies.
eMethods. Detailed Statistical Methodology
eResults. Supplementary Results
eFigure 1. Conceptual Framework of the Attributable Rate Difference (ARD) with A Worked Example
eFigure 2. Study Population and Flow Diagram
eFigure 3. Sex-Specific Age-Standardized Incidence Rates of Cancer
eFigure 4. Sex Disparities for the Incidence of Non−sex-specific Cancers Combined (by 5-Year Age Group)
eFigure 5. Sex-Specific Cumulative Incidence and Mortality of Non−sex-specific Cancers Combined (40-84 Years)
eFigure 6. Sex-Specific Age-Standardized Mortality Rates of Cancer
eFigure 7. Sex Disparities for the Mortality of Non−sex-specific Cancers Combined (by 5-Year Age Group)
eFigure 8. Male-to-Female Incidence Rate Ratios and Mortality Rate Ratios by Cancer Site
eTable 1. ICD-9 and ICD-10 Codes for Non−sex-specific Cancer Types and Number of New Cases and Deaths for Each Outcome
eTable 2. Risk Factors Used to Calculate Population Attributable Fractions for Each Cancer Site eTable 3. Summary of Risk Factors Used to Calculate Population Attributable Fractions
eTable 4. Demographics and Distributions of Risk Factors, by Study Population
eTable 5. Missing Data and Follow-Up Summary by Population and Sex
eTable 6. Comparison of UKB Participants With and Without Complete Data on Total Physical Activity
eTable 7. Male-to-Female Mortality Rate Ratios and Differences in Age-standardized Mortality Rate by Cancer Site
eTable 8. 5-year and 10-year Population Attributable Fractions (PAFs), Attributable Rate Differences (ARDs) and Attributable Proportion (AP) for Cancer Incidence
eTable 9. 5-year Population Attributable Fractions (PAFs) and Attributable Rate Differences (ARDs) for Cancer Mortality
eTable 10. Cause-Specific Hazard Ratios (HRs) and Fine-Gray Subdistribution Hazard Ratios (sdHRs) for Associations between Risk Factors and Cancer Outcomes
eTable 11. 5-year Population Attributable Fractions under Complete-Case Analysis vs Multiple Imputation for Total Physical Activity (UK Biobank)
Data Sharing Statement
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Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
eMethods. Detailed Statistical Methodology
eResults. Supplementary Results
eFigure 1. Conceptual Framework of the Attributable Rate Difference (ARD) with A Worked Example
eFigure 2. Study Population and Flow Diagram
eFigure 3. Sex-Specific Age-Standardized Incidence Rates of Cancer
eFigure 4. Sex Disparities for the Incidence of Non−sex-specific Cancers Combined (by 5-Year Age Group)
eFigure 5. Sex-Specific Cumulative Incidence and Mortality of Non−sex-specific Cancers Combined (40-84 Years)
eFigure 6. Sex-Specific Age-Standardized Mortality Rates of Cancer
eFigure 7. Sex Disparities for the Mortality of Non−sex-specific Cancers Combined (by 5-Year Age Group)
eFigure 8. Male-to-Female Incidence Rate Ratios and Mortality Rate Ratios by Cancer Site
eTable 1. ICD-9 and ICD-10 Codes for Non−sex-specific Cancer Types and Number of New Cases and Deaths for Each Outcome
eTable 2. Risk Factors Used to Calculate Population Attributable Fractions for Each Cancer Site eTable 3. Summary of Risk Factors Used to Calculate Population Attributable Fractions
eTable 4. Demographics and Distributions of Risk Factors, by Study Population
eTable 5. Missing Data and Follow-Up Summary by Population and Sex
eTable 6. Comparison of UKB Participants With and Without Complete Data on Total Physical Activity
eTable 7. Male-to-Female Mortality Rate Ratios and Differences in Age-standardized Mortality Rate by Cancer Site
eTable 8. 5-year and 10-year Population Attributable Fractions (PAFs), Attributable Rate Differences (ARDs) and Attributable Proportion (AP) for Cancer Incidence
eTable 9. 5-year Population Attributable Fractions (PAFs) and Attributable Rate Differences (ARDs) for Cancer Mortality
eTable 10. Cause-Specific Hazard Ratios (HRs) and Fine-Gray Subdistribution Hazard Ratios (sdHRs) for Associations between Risk Factors and Cancer Outcomes
eTable 11. 5-year Population Attributable Fractions under Complete-Case Analysis vs Multiple Imputation for Total Physical Activity (UK Biobank)
Data Sharing Statement
