| Literature DB >> 30830935 |
Kumiko T Kanatani1,2, Takeo Nakayama2, Yuichi Adachi3, Kei Hamazaki4, Kazunari Onishi5, Yukuo Konishi6, Yasuyuki Kawanishi6, Tohshin Go1, Keiko Sato1,7, Youichi Kurozawa5, Hidekuni Inadera4, Ikuo Konishi8, Satoshi Sasaki9, Hiroshi Oyama10.
Abstract
BACKGROUND: As a consequence of indoor occupations and reduced exposure to sunlight, concerns have been raised that vitamin D deficiency is widespread in developed countries. Vitamin D is known to be associated with increased risks of morbidity and mortality in various diseases.Entities:
Mesh:
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Year: 2019 PMID: 30830935 PMCID: PMC6398852 DOI: 10.1371/journal.pone.0213264
Source DB: PubMed Journal: PLoS One ISSN: 1932-6203 Impact factor: 3.240
Fig 1Serum samples analyzed in the sub-study of the Japan Environment and Children’s Study (JECS).
Characteristics of study cohort.
| Entire cohort dataset | Reasonable answer dataset | |
|---|---|---|
| 31.4±4.7 | 31.7±4.6 | |
| 158.4±5.3 | 158.6±5.3 | |
| 20.8±3.2 | 20.9±2.8 | |
| 5.5±2.8 | 5.3±2.8 | |
| n (%) | n (%) | |
| Yes | 79 (5.0) | 62 (5.1) |
| No | 1465 (92.0) | 1148 (94.9) |
| No response | 48 (3.0) | 0 (0) |
| n (%) | n (%) | |
| 828 (52.0) | 649 (53.6) | |
| Agree | 631 (39.6) | 495 (40.9) |
| Cannot decide | 70 (4.4) | 55 (4.6) |
| Disagree | 10 (0.6) | 8 (0.8) |
| Totally disagree | 2 (0.1) | 2 (0.2) |
| No response | 51 (3.2) | 1 (0.1) |
| n (%) | n (%) | |
| 26 (1.6) | 20 (1.7) | |
| No | 1518 (95.4) | 1190 (98.4) |
| No response | 48 (3.0) | 0 (0) |
| n (%) | n (%) | |
| 36 (2.3) | 26 (2.2) | |
| No | 1508 (94.7) | 1184 (97.9) |
| No response | 48 (3.0) | 0 (0) |
| n (%) | n (%) | |
| Always | 36 (2.3) | 33 (2.7) |
| Only in summer | 767 (48.2) | 706 (58.4) |
| Rarely | 466 (29.3) | 422 (34.9) |
| No response | 323 (20.3) | 49 (4.1) |
| n (%) | n (%) | |
| Rarely | 239 (15.0) | 216 (17.9) |
| Once to twice a week | 343 (21.6) | 314 (26.0) |
| Three to four times a week | 333 (20.9) | 309 (25.5) |
| More than 5 times a week | 407 (25.6) | 371 (30.7) |
| No response | 270 (17.0) | 0 (0) |
| n (%) | n (%) | |
| Rarely | 242 (15.2) | 218 (18.0) |
| Once a month | 57 (3.6) | 53 (4.4) |
| Twice to three times a month | 341 (21.4) | 315 (26.0) |
| Every weekend | 659 (41.4) | 601 (49.7) |
| No response | 293 (18.4) | 23 (1.9) |
| n (%) | n (%) | |
| Burns easily, never tans | 109 (6.9) | 93 (7.7) |
| Burns easily, tans minimally with difficulty | 521 (32.7) | 472 (39.0) |
| Burns moderately, tans moderately | 465 (29.2) | 431 (35.6) |
| Burns minimally, tans moderately and easily | 122 (7.7) | 110 (9.1) |
| Rarely burns, tans profusely | 6 (0.4) | 5 (0.4) |
| No response | 369 (23.2) | 99 (8.2) |
| n (%) | n (%) | |
| Asthma | 182 (11.4) | 143 (11.8) |
| Allergic rhinitis | 631 (39.6) | 504 (41.7) |
| Atopic dermatitis | 273 (17.2) | 222 (18.4) |
| n (%) | n (%) | |
| Yes | 6 (0.4) | 4 (0.3) |
| No | 1521 (95.5) | 1193 (98.6) |
| No response | 65 (4.1) | 13 (1.1) |
| n (%) | n (%) | |
| Never | 1400 (87.9) | 1105 (91.3) |
| One to two times a month | 84 (5.3) | 61 (5.0) |
| Three to four times a week | 52 (3.3) | 40 (3.3) |
| More than five times a week | 5 (0.3) | 2 (0.2) |
| No response | 51 (3.2) | 2 (0.2) |
| n (%) | n (%) | |
| Never smoked | 1009 (65.0) | 784 (64.8) |
| Stopped before pregnancy | 382 (24.0) | 299 (24.7) |
| Stopped during pregnancy | 138 (8.7) | 100 (8.3) |
| Current smoker | 37 (2.3) | 24 (2.0) |
| No response | 26 (1.6) | 3 (0.3) |
| n (%) | n (%) | |
| Never smoked | 508 (31.9) | 394 (32.6) |
| Stopped before pregnancy | 409 (25.7) | 320 (26.5) |
| Stopped after pregnancy | 28 (1.8) | 17 (1.4) |
| Current smoker | 608 (38.2) | 467 (38.6) |
| No response | 39 (2.5) | 12 (1.0) |
| n (%) | n (%) | |
| Junior high school | 42 (2.6) | 31 (2.6) |
| High school | 369 (23.2) | 268 (22.2) |
| Vocational school | 330 (20.7) | 227 (18.8) |
| College (2 years) | 311 (19.5) | 246 (20.3) |
| High vocational School | 21 (1.3) | 17 (1.4) |
| College (4 years) | 453 (28.5) | 382 (31.6) |
| Graduate school | 39 (2.5) | 36 (3.0) |
| No response | 27 (1.7) | 3 (0.3) |
| n (%) | n (%) | |
| Under $20,000 | 51 (3.2) | 30 (2.5) |
| $20,000–40,000 | 433 (27.2) | 328 (27.1) |
| $40,000–60,000 | 530 (33.3) | 417 (34.5) |
| $60,000–80,000 | 271 (17.0) | 220 (18.2) |
| $80,000–100,000 | 111 (7.0) | 93 (7.7) |
| Above $100,000 | 82 (5.2) | 64 (5.3) |
| No response | 114 (7.2) | 58 (4.8) |
a Values are expressed as the mean ± SD.
b Data from Japan Environment and Children's Study (JECS).
c Adjusted by total energy.
d No response corresponds to those who did not return the questionnaire.
Fig 2Seasonal changes in serum 25(OH)D levels.
Serum 25(OH) levels (least square means; LS means and 95% confidence intervals; 95%CI) in univariate models.
| LS means | 95% CI | Adjusted P value | ||||
|---|---|---|---|---|---|---|
| Winter (Jan) | 13.5 | 13.1 | − | 13.9 | ref | |
| Spring (Apr) | 12.7 | 12.3 | − | 13.1 | .006 | |
| Summer (Jul) | 16.3 | 15.9 | − | 16.8 | < .0001 | |
| Autumn (Oct) | 20.2 | 19.6 | − | 20.7 | < .0001 | |
| Kyoto (N35) | 15.1 | 14.6 | − | 15.6 | ref | |
| Toyama (N36) | 16.1 | 15.7 | − | 16.5 | .008 | |
| Tottori (N35.5) | 14.4 | 13.8 | − | 15.0 | .105 | |
| < .0001 | ||||||
| Rarely | 13.8 | 13.2 | − | 14.4 | ref | |
| Once a week | 14.8 | 14.2 | − | 15.4 | .062 | |
| Two to three times a week | 15.5 | 14.9 | − | 16.1 | .001 | |
| More than four times a week | 16.8 | 16.2 | − | 17.4 | < .0001 | |
| < .0001 | ||||||
| Rarely | 14.0 | 13.3 | − | 14.6 | ref | |
| Once a month | 15.7 | 14.3 | − | 17.3 | .082 | |
| Two to three times a month | 15.1 | 14.5 | − | 15.7 | .038 | |
| Every week | 16.0 | 15.6 | − | 16.5 | < .0001 | |
| .188 | ||||||
| Always | 13.9 | 12.3 | − | 15.8 | ref | |
| Only in summer | 15.3 | 14.9 | − | 15.7 | .186 | |
| Rarely | 15.6 | 15.1 | − | 16.1 | .106 | |
| .293 | ||||||
| Burns easily, never tans | 14.5 | 13.5 | − | 15.6 | .203 | |
| Burns easily, tans minimally with difficulty | 15.7 | 15.2 | − | 16.2 | ref | |
| Burns moderately, tans moderately | 15.2 | 14.7 | − | 15.7 | .996 | |
| Burns minimally, tans moderately and easily | 15.8 | 14.8 | − | 16.9 | .999 | |
| Rarely burns, tans profusely | 15.9 | 11.9 | − | 21.2 | .057 | |
| < .0001 | ||||||
| 1st quartile (–3.8μg/day) | 14.6 | 14.0 | − | 15.1 | ref | |
| 2nd quartile (3.8–5.2μg/day) | 15.0 | 14.5 | − | 15.6 | .486 | |
| 3rd quartile (5.2–6.9μg/day) | 15.7 | 15.1 | − | 16.3 | .019 | |
| 4th quartile (6.9 –μg/day) | 17.0 | 16.4 | − | 17.6 | < .0001 | |
| No | 15.3 | 15.0 | − | 15.6 | ref | |
| Yes | 19.4 | 17.9 | − | 21.0 | < .0001 | |
| 1st trimester | 14.5 | 14.0 | − | 15.1 | < .0001 | |
| 2nd trimester | 16.2 | 15.8 | − | 16.7 | ref | |
| At delivery | 15.0 | 14.6 | − | 15.4 | < .0001 | |
| .032 | ||||||
| <25 years | 14.1 | 13.1 | − | 15.1 | .032 | |
| 25–35 years | 15.4 | 15.1 | − | 16.2 | ref | |
| >35 years | 15.7 | 15.1 | − | 15.8 | .759 | |
| .519 | ||||||
| <18.5 | 15.1 | 14.4 | − | 15.7 | .439 | |
| 18.5–25 | 15.5 | 15.2 | − | 15.8 | ref | |
| >25 | 15.4 | 14.5 | − | 16.4 | .974 | |
| No | 15.4 | 15.1 | − | 15.7 | ref | |
| Yes | 15.4 | 14.6 | − | 16.3 | .974 | |
| No | 15.4 | 15.1 | − | 15.8 | ref | |
| Yes | 15.4 | 14.9 | − | 15.8 | .860 | |
| No | 15.4 | 15.1 | − | 15.7 | ref | |
| Yes | 15.4 | 14.7 | − | 16.1 | .905 | |
| Yes | 18.9 | 14.0 | − | 25.5 | .198 | |
| No | 15.5 | 15.2 | − | 15.8 | ref | |
| .428 | ||||||
| Never | 15.6 | 15.3 | − | 15.9 | .514 | |
| One to three times a month | 14.8 | 13.7 | − | 16.0 | ref | |
| One to four times a week | 14.7 | 13.3 | − | 16.3 | .999 | |
| More than five times a week | 17.1 | 12.1 | − | 24.1 | .782 | |
| .1194 | ||||||
| Under $20,000 | 15.0 | 13.7 | − | 16.5 | .9996 | |
| $20,000–40,000 | 15.2 | 14.7 | − | 15.7 | ref | |
| $40,000–60,000 | 15.7 | 15.3 | − | 16.2 | .5378 | |
| $60,000–80,000 | 15.6 | 15.0 | − | 16.3 | .8372 | |
| $80,000–100,000 | 15.6 | 14.6 | − | 16.6 | .9588 | |
| Above $100,000 | 16.0 | 14.9 | − | 17.2 | .6913 | |
| .015 | ||||||
| Never smoked | 15.6 | 15.3 | − | 16.0 | ref | |
| Stopped before pregnancy | 15.6 | 15.1 | − | 16.2 | 1.00 | |
| Stopped during pregnancy | 14.3 | 13.4 | − | 15.2 | .018 | |
| Current smoker | 14.0 | 12.5 | − | 15.8 | .204 | |
| .019 | ||||||
| Never smoked | 15.7 | 15.2 | − | 16.2 | ref | |
| Stopped before pregnancy | 15.8 | 15.3 | − | 16.4 | .971 | |
| Stopped after pregnancy | 17.0 | 14.8 | − | 19.6 | .567 | |
| Current smoker | 14.9 | 14.5 | − | 15.4 | .068 | |
Entire cohort dataset (excluding non-responders for each question).
All values are from univariate linear mixed models, with 25(OH)D natural log-transformed.
LS means and 95%CIs are shown as exponentials of log-transformed 25(OH)D.
For variables with more than three groups, p values are adjusted by Dunnett.
a P values for trend.
b Reasonable answer dataset, total energy adjusted by residual method.
Fig 3Serum 25(OH)D levels during each month in relation to the frequency of sunlight exposure.
Linear mixed model with random effect of repeated measurements. Adjusted by location, dietary vitamin D intake, dietary calorie intake, vitamin D supplementation, pregnancy trimester, and if they live with children.
Serum 25(OH) levels (least square means; LS means and 95% confidence intervals; 95%CI) in multivariate models.
| LS means | 95%CI | p value | |||
|---|---|---|---|---|---|
| < .001 | |||||
| Kyoto (N35) | 16.4 | 15.6 | - | 17.2 | ref |
| Toyama (N36) | 17.7 | 16.8 | - | 18.4 | .002 |
| Tottori (N35.5) | 16.0 | 15.1 | - | 16.9 | .570 |
| < .001 | |||||
| Winter (Jan) | 14.8 | 14.1 | - | 15.5 | ref |
| Spring (Apr) | 13.8 | 13.2 | - | 14.6 | .009 |
| Summer (Jul) | 17.3 | 16.4 | - | 18.2 | < .0001 |
| Autumn (Oct) | 21.7 | 20.6 | - | 22.7 | < .0001 |
| < .0001 | |||||
| 1st trimester | 16.1 | 15.3 | - | 17.0 | < .0001 |
| 2nd trimester | 17.7 | 17.0 | - | 18.6 | Ref |
| At delivery | 16.1 | 15.4 | - | 16.8 | < .0001 |
| No | 14.7 | 14.4 | - | 15.0 | Ref |
| Yes | 19.0 | 17.5 | - | 20.5 | < .0001 |
| < .0001 | |||||
| 1st quartile (– 3.8μg/day) | 15.4 | 14.6 | - | 16.3 | ref |
| 2nd quartile (3.8–5.2μg/day) | 16.4 | 15.5 | - | 17.3 | .052 |
| 3rd quartile (5.2–6.9μg/day) | 16.7 | 15.9 | - | 17.6 | .006 |
| 4th quartile (6.9 – μg/day) | 18.1 | 17.2 | - | 19.1 | < .0001 |
| < .0001 | |||||
| Rarely | 15.1 | 14.3 | - | 16.0 | ref |
| Once a week | 16.2 | 15.4 | - | 17.1 | .017 |
| Two to three times a week | 16.9 | 16.1 | - | 17.9 | .0001 |
| More than four times a week | 18.4 | 17.5 | - | 19.4 | < .0001 |
Reasonable answer dataset
Multivariate linear mixed models, with 25(OH)D natural log-transformed.
LS means and 95%CIs are shown as exponentials of natural log-transformed 25(OH)D.
For variables with more than three groups, the p values are adjusted by Dunnett.
a Adjusted by total energy by residual method.
Fig 4Serum 25(OH)D levels during each month in relation to the daily dietary intake of vitamin D.
Linear mixed model with random effect of repeated measurements. Adjusted by location, frequency of sunlight exposure, dietary calorie intake, vitamin D supplementation, pregnancy trimester, and if they live with children. Average of 1st quartile was 2.5μg/day, and average of 4th quartile was 9.4μg/day.
Fig 5Serum 25(OH)D levels in Kyoto, Toyama, and Tottori in relation to the sampled months.
Linear mixed model with random effect of repeated measurements. Adjusted by location, frequency of sunlight exposure, dietary vitamin D intake, dietary calorie intake, vitamin D supplementation, pregnancy trimester, and if they live with children.