Association between perfluoroalkyl substance concentrations and blood pressure in adolescents

https://doi.org/10.1016/j.envpol.2019.112971Get rights and content

Highlights

  • 2251 adolescents were used to examine associations of polyfluoroalkyl chemicals with blood pressure levels.

  • Positive associations were found between blood PFOS and diastolic blood pressure in males.

  • Restricted cubic spline models showed no significant associations between PFOS and blood pressure.

Abstract

The effects of exposure to some environmental chemicals on blood pressure have been determined, but the association between non-occupational exposure to perfluoroalkyl substances (PFASs) and blood pressure in adolescents remains unknown. The association between blood pressure and PFAS concentrations was studied by analysing data from 2251 participants filtered from the population enrolled in the National Health and Nutrition Examination Survey (NHANES) from 2003 to 2012. After adjusting for age, sex, race, BMI, cotinine level, dietary intake of calcium, caloric intake, sodium consumption, potassium consumption and sampling year, we estimated the coefficients (betas) and 95% confidence intervals (CIs) for the relationship between PFAS concentrations and blood pressure with multiple linear regression models. Potential non-linear relationships were assessed with restricted cubic spline models. Blood levels of perfluorooctane sulfonic acid (PFOS) had a strong positive association with diastolic blood pressure (DBP) in adolescents in the linear model, while the result was not significant in the non-linear model. No significant association was observed between the concentration of any other PFASs and blood pressure. According to the fully adjusted linear regression model (P = 0.041), the mean DBP values in boys in the higher PFOS quintile were 2.70% greater than the mean DBP values of boys in the lowest PFOS quintile. Furthermore, serum PFOS concentrations predominantly affected blood pressure in male adolescents compared with female adolescents. These results provide epidemiological evidence of PFOS-related increases in DBP. Further research is needed to address related issues.

Introduction

Hypertension, or elevated blood pressure, is a global public health problem. According to documents issued by the World Health Organization (WHO), hypertension is defined as a systolic blood pressure (SBP) value ≥ 140 mmHg and/or a diastolic blood pressure (DBP) value ≥ 90 mmHg. The global number of hypertensive patients increased to 1 billion by 2008. In general, the prevalence was higher in males than in females. According to a survey published by the American Medical Association (AMA), the systolic blood pressure of 3.5 billion adults ranges from at least 110–115 mmHg, while 874 million adults have systolic blood pressure values above 140 mmHg (Forouzanfar et al., 2017). In addition, many hypertensive patients remain undiagnosed due to a lack of symptoms in the early stages. Alarmingly, after the American Academy of Pediatrics (AAP) released new practical clinical guidelines in 2017 in which they redefined hypertension as BP ≥ 130/80 mmHg or the reported use of anti-hypertensive medication among adolescents aged 12–19 years, 795 thousand young people were reclassified as hypertensive patients (Jackson et al., 2018). An increase in the prevalence of hypertension among adolescents is expected, with a higher prevalence in males (Rao, 2016). Therefore, determining the risk factors for hypertension is critical, and some new risk factors have been reported in recent years. In addition to the risk factors for adults published by the WHO in 2013, such as ageing, population growth and behaviours, youths who were male, relatively older and obese tended to have high blood pressure (Anyaegbu and Dharnidharka, 2014; Jackson et al., 2018). Additionally, a number of studies revealed that environmental factors are nonnegligible contributors to high blood pressure, especially perfluoroalkyl substances (PFASs) (Li et al., 2013; Lin et al., 2011; Yorifuji et al., 2010).

PFASs are synthetic organic compounds and include perfluorooctanoic acid (PFOA), perfluorooctane sulfonic acid (PFOS), perfluorohexane sulfonic acid (PFHxS), 2-(N-ethyl-perfluorooctane sulfonamido) acetate (EPAH), and 2-(N-methyl-perfluorooctane sulfonamido) acetate (MPAH). PFASs have been widely used in commercial applications and various manufacturing industries, including the manufacture of surfactants, paper, lubricants, textile coatings, and water and oil repellents in cosmetics, clothing, food packaging and furnishings (Lindstrom et al., 2011; Prevedouros et al., 2006). On account of their stable biology, physics and chemistry, PFASs accumulate and can be biomagnified through the trophic chain (Tomy et al., 2004). According to the national biological monitoring survey report, PFOA, PFOS and other perfluorooctanoic acids are emerging as human pollutants, and they are not only commonly detected in surface water, soil, wastewater and indoor environmental sources but also in human blood in vivo. Some studies have reported that PFASs, especially PFOA and PFOS, could harm animals to a certain degree, with effects including neurotoxicity (Salgado et al., 2016), a decrease in the Ser9 phosphorylation of glycogen synthase kinase-3β (Dong et al., 2016), inhibition of the differentiation of neural stem cells (Wan Ibrahim et al., 2013) and development of sex hormone disorders (Chen et al., 2016).

In addition, several studies have demonstrated that PFASs are correlated with hypertension in adults (Bao et al., 2017; Min et al., 2012). A study on young hypertensive patients showed that teenagers diagnosed with hypertension had higher levels of PFASs than those not diagnosed with hypertension, but the study did not further analyse the relationship between PFASs and hypertension (Min et al., 2012). The relationships between hypertension in teenagers and the concentrations of PFASs are still unclear. Therefore, our study focused on the correlations between the concentrations of PFASs and hypertension in adolescents. Interestingly, the results of the study revealed that the concentration of PFOS was positively associated with diastolic blood pressure in adolescent boys.

Section snippets

Subjects

We used publicly available data regarding subjects who were recruited for the National Health and Nutrition Examination Survey (NHANES). The data were from five cycles of the NHANES (2003–2004, 2005–2006, 2007–2008, 2009–2010, and 2011–2012). The NHANES website [https://www.cdc.gov/nchs/nhanes/] presents the detailed survey design, methods and available data. In brief, the NHANES study population is representative of the civilian non-institutionalised U.S. population. Mobile examination centers

Results

The demographics of the study subjects is shown in Table 1. Differential significance was not found in age, race, BMI and PIR.

Table 2 shows the results of the univariate linear regression analyses of the relationships among BP, serum concentrations of PFASs and the potential confounders. Most of the confounders were significantly associated. However, calcium intake and PIR were not significantly associated; thus, we did not include them in the multiple linear regression analysis or the

Discussion

This population-based study was the first to identify the association between low-dose exposure to PFOS and increased DBP in adolescents, especially in males.

However, some studies had conflicting conclusions. Research on the offspring of pregnant rats exposed to diverse chemicals has shown that PFOS is associated with hypertension, especially systolic blood pressure. Male offspring in the PFOS group had higher systolic blood pressure values than those of the controls at 7 weeks of age, while a

Conclusion

Our study found that low-dose exposure to PFOS is related to elevated diastolic blood pressure in male adolescents and that the effects of PFOS on blood pressure exhibited a sex difference. The mechanism underlying the effect of PFOS on hypertension may be related to hepatocytes, hypercholesterolaemia and high peripheral resistance, with decreased levels of thyroid hormones and aldosterone increasing DBP.

Funding

This work was supported by the Maternal and Child Health Research Project of Jiangsu Province (F201755); the China Postdoctoral Science Foundation (2018M630585); the Key Project of Science and Technology Development Fund of Nanjing Medical University (2017NJMUZD060); the National Key Research and Development Program of China (2016YFC1101001, 2017YFC1308105); the Nanjing Medical University School Project (NMUC2018012A); and a Key Project supported by the Medical Science and Technology

Declaration of interests

The authors declare that they have no known competing financial interests or personal relationships that could have appeared to influence the work reported in this paper.

The authors declare the following financial interests/personal relationships which may be considered as potential competing interests:

Disclosure statement

The authors declare that they have no competing interests.

Acknowledgement

Xu C and Mo XM designed the study protocol. Xu C and Ma SY conducted the research and performed the data analysis under the close supervision of Wang ZQ, Zhang YX, Shu YQ and Mo XM. Ma J provided language help. The manuscript was drafted by Ma SY and proofread by Xu C.

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    This paper has been recommended for acceptance by Eddy Y. Zeng.

    1

    These authors contributed equally to the present study and should be regarded as joint first authors.

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