Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2019 Sep;26(27):28256-28269.
doi: 10.1007/s11356-019-06003-2. Epub 2019 Jul 31.

Phthalates and asthma in children and adults: US NHANES 2007-2012

Affiliations

Phthalates and asthma in children and adults: US NHANES 2007-2012

Chinonso Christian Odebeatu et al. Environ Sci Pollut Res Int. 2019 Sep.

Erratum in

Abstract

Environmental exposure to phthalates may contribute to an increased risk of asthma in children and adults. We aimed to assess the direction and strength of the association between urinary phthalates metabolites and current asthma in children and adults that participated in the National Health and Nutrition Examination Survey (NHANES) 2007-2012. Data on ten urinary phthalate metabolites, self-reported questionnaires, spirometry measures, and covariates were obtained from 7765 participants (28.1% were children aged 6-17 years) taking part in the NHANES 2007-2012. Asthma was assessed using self-reported questionnaires for children and adults, and via spirometry measures for adults alone. We used crude and adjusted logistic regression models to estimate the odds ratios (ORs) and 95% confidence interval (CI) per one log10 unit change in the concentration of phthalate metabolites. We further modeled the effect modification by sex. Out of 10 metabolites, only mono-benzyl phthalate (MBzP) was positively associated with the prevalence of self-reported asthma in children, after adjusting for a range of potential confounders (odds ratio 1.54; 95% confidence interval 1.05-2.27). No significant relationship was observed for adults. The association of mono-ethyl phthalate (MEP) was modified by sex, with significantly increased odds of asthma among males [boys (2.00; 1.14-3.51); adult males (1.32; 1.04-1.69)]. While no other phthalates showed a positive relationship with current asthma in males, mono-(carboxynonyl) phthalate (MCNP) and mono-(3-carboxylpropyl) phthalate (MCPP) were inversely associated with spirometrically defined asthma in adult females. A sex-specific relationship in adults was evident when spirometry, but not self-reported measures were used to define asthma. We found no clear association between exposure to phthalates and current asthma, except for a significant relationship between MBzP metabolites and self-reported asthma in children. As a result, exposure to phthalates and asthma development and/or exacerbations remains controversial, suggesting a need for a well-designed longitudinal study.

Keywords: Adult asthma; Childhood asthma; Mono-benzyl phthalate; NHANES; Phthalate metabolites.

PubMed Disclaimer

Conflict of interest statement

The authors declare that they have no competing interests.

Figures

Fig. 1
Fig. 1
a Model 1 (crude) - associations of urinary phthalate metabolites with self-reported asthma in children, NHANES 2007–2012. Logistic regression modeling was used to access the effect of individual phthalate metabolites on asthma prevalence, with an odds ratio (OR) presented for 1 log10 unit change in urinary phthalate concentration. b Model 2 (adjusted)—associations of urinary phthalate metabolites with self-reported asthma in children, NHANES 2007–2012. Logistic regression modeling was used to access the effect of individual phthalate metabolites on asthma prevalence, with an OR presented for 1 log10 unit change in urinary phthalate concentration. MEP mono-ethyl phthalate, MiBP mono-isobutyl phthalate, MnBP mono-n-butyl phthalate, MBzP mono-benzyl phthalate, MCNP mono-(carboxynonyl) phthalate, MCPP mono-(3-carboxylpropyl) phthalate, ΣDEHP molar sum of DEHP metabolites (MEHP, MEHHP, MECPP and MEOHP). All models were adjusted for age, sex, ethnicity/race, waist circumference, cotinine, poverty and urinary creatinine
Fig. 2
Fig. 2
Associations between urinary phthalate metabolites and asthma (self-reported) in children stratified by sex. Logistic regression modeling was used to access the effect of individual phthalate metabolites on asthma prevalence, with odds ratio (OR) presented for 1 log10 unit change in urinary phthalate concentration. MEP mono-ethyl phthalate, MiBP mono-isobutyl phthalate, MnBP mono-n-butyl phthalate, MBzP mono-benzyl phthalate, MCNP mono-(carboxynonyl) phthalate, MCPP mono-(3-carboxylpropyl) phthalate, ΣDEHP molar sum of DEHP metabolites (MEHP, MEHHP, MECPP and MEOHP). All models were adjusted for age, race/ethnicity, waist circumference, poverty, urinary creatinine and cotinine
Fig. 3
Fig. 3
a Model 1 (crude)—associations of urinary phthalate metabolites with self-reported asthma in adults, NHANES 2007–2012. Logistic regression modeling was used to access the effect of individual phthalate metabolites on asthma prevalence, with odds ratio (OR) presented for 1 log10 unit change in urinary phthalate concentration. b Model 2 (adjusted) - associations of urinary phthalate metabolites with self-reported asthma in children, NHANES 2007–2012. Logistic regression modeling was used to access the effect of individual phthalate metabolites on asthma prevalence, with odds ratio (OR) presented for 1 log10 unit change in urinary phthalate concentration. MEP mono-ethyl phthalate, MiBP mono-isobutyl phthalate, MnBP mono-n-butyl phthalate, MBzP mono-benzyl phthalate, MCNP mono-(carboxynonyl) phthalate, MCPP mono-(3-carboxylpropyl) phthalate, ΣDEHP molar sum of DEHP metabolites (MEHP, MEHHP, MECPP and MEOHP). All models were adjusted for age, sex, ethnicity/race, waist circumference, cotinine, poverty and urinary creatinine
Fig. 4
Fig. 4
Associations between urinary phthalate metabolites and asthma (self-reported) in adults stratified by sex. Logistic regression modeling was used to access the effect of individual phthalate metabolites on asthma prevalence, with odds ratio (OR) presented for 1 log10 unit change in urinary phthalate concentration. MEP mono-ethyl phthalate, MiBP mono-isobutyl phthalate, MnBP mono-n-butyl phthalate, MBzP mono-benzyl phthalate, MCNP mono-(carboxynonyl) phthalate, MCPP mono-(3-carboxylpropyl) phthalate, ΣDEHP molar sum of DEHP metabolites (MEHP, MEHHP, MECPP and MEOHP). All models were adjusted for age, race/ethnicity, waist circumference, urinary creatinine and cotinine
Fig. 5
Fig. 5
a Model 1 (crude)—associations of urinary phthalate metabolites with current asthma (spirometry measure) in adults, NHANES 2007–2012. Logistic regression modeling was used to access the effect of individual phthalate metabolites on asthma prevalence, with odds ratio (OR) presented for 1 log10 unit change in urinary phthalate concentration. b Model 2 (adjusted)—associations of urinary phthalate metabolites with current asthma (spirometry measure) in adults, NHANES 2007–2012. Logistic regression modeling was used to access the effect of individual phthalate metabolites on asthma prevalence, with odds ratio (OR) presented for 1 log10 unit change in urinary phthalate concentration. MEP mono-ethyl phthalate, MiBP mono-isobutyl phthalate, MnBP mono-n-butyl phthalate, MBzP mono-benzyl phthalate, MCNP mono-(carboxynonyl) phthalate, MCPP mono-(3-carboxylpropyl) phthalate, ΣDEHP molar sum of DEHP metabolites (MEHP, MEHHP, MECPP and MEOHP). All models were adjusted for age, sex, ethnicity/race, waist circumference, cotinine, poverty, and urinary creatinine
Fig. 6
Fig. 6
Associations between urinary phthalate metabolites and current asthma (spirometry measure in adults stratified by sex. Logistic regression modeling was used to access the effect of individual phthalate metabolites on asthma prevalence, with odds ratio (OR) presented for 1 log10 unit change in urinary phthalate concentration. MEP mono-ethyl phthalate, MiBP mono-isobutyl phthalate, MnBP mono-n-butyl phthalate, MBzP mono-benzyl phthalate, MCNP mono-(carboxynonyl) phthalate, MCPP mono-(3-carboxylpropyl) phthalate, ΣDEHP molar sum of DEHP metabolites (MEHP, MEHHP, MECPP and MEOHP). All models were adjusted for age, race/ethnicity, waist circumference, urinary creatinine and cotinine

Similar articles

Cited by

References

    1. Abo-Zaid G, Sharpe RA, Fleming LE, Depledge M, Osborne NJ. Association of infant eczema with childhood and adult asthma: analysis of data from the 1958 birth cohort study. Int J Environ Res Public Health. 2018;15(7):1415. doi: 10.3390/ijerph15071415. - DOI - PMC - PubMed
    1. Alfardan AS, Nadeem A, Ahmad SF, Al-Harbi NO, Al-Harbi MM, AlSharari SD. Plasticizer, di (2-ethylhexyl) phthalate (DEHP) enhances cockroach allergen extract-driven airway inflammation by enhancing pulmonary Th2 as well as Th17 immune responses in mice. Environ Res. 2018;164:327–339. - PubMed
    1. Almqvist C, Worm M, Leynaert B. Impact of gender on asthma in childhood and adolescence: a GA2LEN review. Allergy. 2008;63(1):47–57. - PubMed
    1. Asher MI, Montefort S, Björkstén B, Lai CKW, Strachan DP, Weiland SK, Williams H. Worldwide time trends in the prevalence of symptoms of asthma, allergic rhinoconjunctivitis, and eczema in childhood: ISAAC Phases One and Three repeat multicountry cross-sectional surveys. Lancet. 2006;368(9537):733–743. - PubMed
    1. Bai PY, Wittert G, Taylor AW, Martin SA, Milne RW, Jenkins AJ, Januszewski AS, Shi Z. The association between total phthalate concentration and non-communicable diseases and chronic inflammation in South Australian urban dwelling men. Environ Res. 2017;158:366–372. - PubMed