| Literature DB >> 33569292 |
Dongfang You1, Mingzhi Zhang1, Wenjing He2, Danhua Wang3, Yang Yu1, Zhaolei Yu1, Theis Lange4, Sheng Yang1, Yongyue Wei1,5, Hongxia Ma6,7,8, Zhibin Hu6,7,8, Hongbing Shen6,8, Feng Chen1,5, Yang Zhao1,5,7.
Abstract
BACKGROUND: Epidemiological studies have reported that dietary mineral intake plays an important role on lung cancer risk, but the association of sodium, potassium intake is still unclear.Entities:
Keywords: Lung cancer; Women’s Health Initiative; cancer screening; potassium; sodium
Year: 2021 PMID: 33569292 PMCID: PMC7867772 DOI: 10.21037/tlcr-20-870
Source DB: PubMed Journal: Transl Lung Cancer Res ISSN: 2218-6751
Figure 1The flow diagram describing the population selection process: the PLCO trial (A) and the observational study of the WHI (B).
Baseline characteristics of lung cancer cases and controls in the PLCO trial and the WHI cohort
| Baseline characteristics (mean ± SD) | The PLCO trial | The WHI cohort | |||||
|---|---|---|---|---|---|---|---|
| Confirmed LC | Non-confirmed LC | P valueb | Confirmed LC | Non-confirmed LC | P valueb | ||
| Total (N) | 1,278 | 91,706 | 1,631 | 70,794 | |||
| Potassium intake (g/day)a | 3.25±0.83 | 3.26±0.76 | 0.965 | 2.62±0.63 | 2.66±0.64 | 0.001 | |
| Sodium intake (g/day)a | 2.71±0.70 | 2.74±0.56 | 0.171 | 2.65±0.49 | 2.64±0.49 | 0.349 | |
| Age (year) | 64.04±5.15 | 62.30±5.26 | <0.001 | 64.89±6.72 | 63.34±7.33 | <0.001 | |
| Gender (%) | |||||||
| Female | 42.5 | 51.8 | <0.001 | 100 | 100 | ||
| Male | 57.5 | 48.2 | – | – | |||
| Body mass index (kg/m2) | 26.57±4.37 | 27.27±4.81 | <0.001 | 26.66±5.47 | 27.19±5.82 | <0.001 | |
| Education (%) | |||||||
| Low | 35.4 | 28.6 | <0.001 | 20.3 | 20.9 | 0.041 | |
| Middle | 40.4 | 34.4 | 39.2 | 36.2 | |||
| High | 24.2 | 37.0 | 40.5 | 42.9 | |||
| Cigarette smoking (%) | |||||||
| Never | 8.2 | 48.4 | <0.001 | 18.3 | 53.1 | <0.001 | |
| Former <20 pack-years | 6.7 | 18.8 | 17.3 | 27.0 | |||
| Former ≥20 pack-years | 44.5 | 24.0 | 39.6 | 14.1 | |||
| Current <20 pack-years | 1.1 | 0.8 | 4.4 | 2.4 | |||
| Current ≥20 pack-years | 39.5 | 8.0 | 20.4 | 3.4 | |||
| Alcohol intake (g/day) | 14.76±37.39 | 9.72±25.40 | <0.001 | 7.63±12.92 | 5.53±11.10 | <0.001 | |
| Energy intake (kcal/day) | 1,815.8±800.3 | 1,740.0±733.1 | 0.005 | 1,569.1±576.8 | 1,570.0±596.2 | 0.636 | |
| Diabetes (%) | 7.12 | 6.51 | 0.408 | 5.15 | 5.24 | 0.910 | |
| Family history of lung cancer (%) | 18.78 | 10.59 | <0.001 | ||||
| Family history of cancer (%) | 60.5 | 54.7 | <0.001 | 67.87 | 63.99 | 0.001 | |
SD, standard deviation; LC, lung cancer. a, intake was energy-adjusted. b, P value for difference was tested using Wilcox rank sum test (continuous) or Chi-square test (categorical).
Gender-specific hazard ratios and 95% confidence intervals of lung cancer based on categories of dietary mineral intake
| Continuous | Quintile 1 | Quintile 2 | Quintile 3 | Quintile 4 | Quintile 5 | |
|---|---|---|---|---|---|---|
| Potassium | ||||||
| WHI (female only) | ||||||
| Dietary intakea | 2,619.5 | <2,153.6 | 2,153.6–2,473.8 | 2,473.8–2,768.2 | 2,768.2–3,139.5 | ≥3,139.5 |
| Cases/person-years | 1,631/1,123,470 | 368/207,916 | 336/220,409 | 332/228,708 | 304/231,972 | 291/234,465 |
| Multivariable model HRb | 0.94 (0.87, 1.02) | 1.00 | 0.93 (0.80, 1.08) | 0.92 (0.79, 1.07) | 0.85 (0.73, 0.99) | 0.82 (0.70, 0.97) |
| P value | 0.124 | Ptrendc =0.009 | ||||
| Female in the PLCO | ||||||
| Dietary intakea | 2,943.8 | <2,463.4 | 2,463.4–2,797.0 | 2,797.0–3,096.8 | 3,096.8–3,487.7 | ≥3,487.7 |
| Cases/person-years | 543/390,992 | 123/77,876 | 106/77,994 | 87/77,975 | 103/78,589 | 124/78,558 |
| Multivariable model HRb | 0.96 (0.85, 1.09) | 1.00 | 0.90 (0.69, 1.17) | 0.72 (0.54, 0.96) | 0.83 (0.63, 1.09) | 0.92 (0.72, 1.19) |
| P value | 0.546 | Ptrendc =0.553 | ||||
| Male in the PLCO | ||||||
| Dietary intakea | 3,489.9 | <2,935.9 | 2,935.9–3,319.7 | 3,319.7–3,670.0 | 3,670.0–4,142.0 | ≥4,142.0 |
| Cases/person-years | 735/343,836 | 152/68,795 | 127/68,496 | 145/68,642 | 159/68,905 | 152/68,998 |
| Multivariable model HRb | 1.06 (0.97, 1.17) | 1.00 | 0.93 (0.73, 1.18) | 1.05 (0.83, 1.33) | 1.12 (0.89, 1.41) | 1.05 (0.83, 1.33) |
| P value | 0.188 | Ptrendc =0.348 | ||||
| Sodium | ||||||
| WHI (female only) | ||||||
| Dietary intakea | 2,620.2 | <2,291.5 | 2,291.5–2,522.5 | 2,522.5–2,722.4 | 2,722.4–2,980.3 | ≥2,980.3 |
| Cases/person-years | 1,631/1,123,470 | 337/221,914 | 293/224,463 | 343/224,825 | 313/226,959 | 345/225,309 |
| Multivariable model HRb | 1.10 (0.99, 1.21) | 1.00 | 0.94 (0.80, 1.11) | 1.15 (0.99, 1.35) | 1.05 (0.90, 1.23) | 1.12 (0.96, 1.30) |
| P value | 0.074 | Ptrendc =0.080 | ||||
| Female in the PLCO | ||||||
| Dietary intakea | 2,361.2 | <2,083.6 | 2,083.6–2,280.3 | 2,280.3–2,442.9 | 2,442.9–2,656.4 | ≥2,656.4 |
| Cases/person-years | 543/390,992 | 143/77,508 | 101/78,109 | 106/78,154 | 100/78,802 | 93/78,418 |
| Multivariable model HRb | 0.83 (0.68, 1.01) | 1.00 | 0.80 (0.62, 1.04) | 0.91 (0.70, 1.18) | 0.82 (0.63, 1.07) | 0.71 (0.54, 0.93) |
| P value | 0.057 | Ptrendc =0.022 | ||||
| Male in the PLCO | ||||||
| Dietary intakea | 3,108.9 | <2,732.1 | 2,732.1–2,996.7 | 2,996.7–3,229.6 | 3,229.6–3,551.6 | ≥3551.6 |
| Cases/person-years | 735/343,836 | 155/68,264 | 127/68,502 | 149/68,646 | 159/69,025 | 145/69,399 |
| Multivariable model HRb | 1.19 (1.05, 1.35) | 1.00 | 1.00 (0.78, 1.28) | 1.24 (0.97, 1.57) | 1.33 (1.05, 1.68) | 1.19 (0.93, 1.53) |
| P value | 0.008 | Ptrendc =0.044 | ||||
a, mineral intake was energy-adjusted (mg/day), median intake for continuous and range for quintiles. b, Cox proportional hazard models were used to adjust age, body mass index (kg/m2), energy intake (kcal/day), educational level (3 categories), alcohol consumption (g/day), smoking status (never smokers, former smokers <20 pack-years, former smokers ≥20 pack-years, current smokers <20 pack-years, current smokers ≥20 pack-years), history of diabetes (yes or no), and family history of lung cancer (yes or no) for the PLCO trial or family history of cancer (yes or no) for the WHI cohort. c, test for linear trend was estimated by assigning the median value of sodium or potassium intake in each quintile.
Figure 2Dose-response association between dietary potassium intake (energy-adjusted) and lung cancer risk for females in the WHI cohort (A), females in the PLCO trial (B), the combination of females (C), and males in the PLCO trial (D) using spline smoothed model. Multivariable risk estimate was calculated to adjust all covariates by spline regression with three knots (20th percentiles as the reference, 2,381 mg/day). Blue solid line represented point estimates, dashed lines and shadow area represented 95% confidence intervals. Red solid points and vertical lines represented HRs and 95% CIs of lung cancer based on categories of dietary potassium intake (compared with the lowest quintile), respectively. Black curve showed the kernel density estimates of participants (right y-axis) consuming of potassium.
Figure 3Dose-response association between dietary sodium intake (energy-adjusted) and lung cancer risk for females in the WHI cohort (A), females in the PLCO trial (B), the combination of females (C), and males in the PLCO trial (D) using spline smoothed model. Multivariable risk estimate was calculated to adjust all covariates by spline regression with three knots (20th percentiles as the reference, 2,349 mg/day). Blue solid line represented point estimates, dashed lines and shadow area represented 95% confidence intervals. Red solid points and vertical lines represented HRs and 95% CIs of lung cancer based on categories of dietary sodium intake (compared with the lowest quintile), respectively. Black curve showed the kernel density estimates of participants (right y-axis) consuming of sodium.
Hazard ratios and 95% confidence intervals of lung cancer based on categories of dietary potassium intake for female
| Quintile 1 | Quintile 2 | Quintile 3 | Quintile 4 | Quintile 5 | Ptrendc | |
|---|---|---|---|---|---|---|
| Dietary potassium intakea | <2,253.6 | 2,253.6–2,597.5 | 2,597.5–2,906.6 | 2,906.6–3,297.8 | ≥3,297.8 | |
| PLCO (N=48,025) | ||||||
| Cases/person-years | 78/44,846 | 80/60,993 | 108/78,777 | 106/93,023 | 171/113,353 | |
| Multivariable model HRb | 1.00 | 0.87 (0.63, 1.19) | 0.87 (0.65, 1.18) | 0.71 (0.53, 0.97) | 0.87 (0.66, 1.15) | 0.359 |
| WHI (N=72,425) | ||||||
| Cases/person-years | 461/269,115 | 379/256,249 | 342/228,387 | 230/204,040 | 219/165,679 | |
| Multivariable model HRb | 1.00 | 0.94 (0.82, 1.08) | 0.98 (0.85, 1.13) | 0.75 (0.64, 0.89) | 0.90 (0.76, 1.06) | 0.023 |
| ALL (N=120,450) | ||||||
| Cases/person-years | 539/313,961 | 459/317,242 | 450/307,165 | 336/297,063 | 390/279,032 | |
| Multivariable model HRb | 1.00 | 0.93 (0.82, 1.05) | 0.96 (0.84, 1.09) | 0.75 (0.65, 0.86) | 0.90 (0.79, 1.03) | 0.017 |
| Dietary sodium intakea | <2,186.3 | 2,186.3–2,409.5 | 2,409.5–2,610.6 | 2,610.6–2,871.8 | ≥2,871.8 | |
| PLCO (N=48,025) | ||||||
| Cases/person-years | 184/114,533 | 141/103,569 | 101/80,981 | 75/55,696 | 42/36,213 | |
| Multivariable model HRb | 1.00 | 1.01 (0.81, 1.27) | 0.93 (0.72, 1.19) | 0.95 (0.72, 1.25) | 0.76 (0.54, 1.07) | 0.150 |
| WHI (N=72,425) | ||||||
| Cases/person-years | 234/151,282 | 222/175,731 | 333/220,300 | 387/269,553 | 455/306,604 | |
| Multivariable model HRb | 1.00 | 0.91 (0.75, 1.09) | 1.14 (0.96, 1.36) | 1.10 (0.93, 1.30) | 1.12 (0.95, 1.32) | 0.05 |
| ALL (N=120,450) | ||||||
| Cases/person-years | 418/265,815 | 363/279,300 | 434/301,281 | 462/325,249 | 497/342,817 | |
| Multivariable model HRb | 1.00 | 0.92 (0.80, 1.07) | 1.05 (0.91, 1.21) | 1.04 (0.90, 1.19) | 1.04 (0.91, 1.19) | 0.284 |
a, mineral intake was energy-adjusted (mg/day), median intake for continuous and range for quintiles. b, Cox proportional hazard models were used to adjust age, body mass index (kg/m2), energy intake (kcal/day), educational level (3 categories), alcohol consumption (g/day), smoking status (never smokers, former smokers <20 pack-years, former smokers ≥20 pack-years, current smokers <20 pack-years, current smokers ≥20 pack-years), history of diabetes (yes or no), and family history of cancer (yes or no). c, test for linear trend was estimated by assigning the median value of potassium intake in each quintile.