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Meta-Analysis
. 2023 Aug 14;22(1):56.
doi: 10.1186/s12940-023-01006-6.

Prenatal and childhood exposure to per-/polyfluoroalkyl substances (PFASs) and its associations with childhood overweight and/or obesity: a systematic review with meta-analyses

Affiliations
Meta-Analysis

Prenatal and childhood exposure to per-/polyfluoroalkyl substances (PFASs) and its associations with childhood overweight and/or obesity: a systematic review with meta-analyses

Gianfranco Frigerio et al. Environ Health. .

Abstract

Background: Per-/polyfluoroalkyl substances (PFASs) are persistent organic pollutants and suspected endocrine disruptors.

Objective: The aim of this work was to conduct a systematic review with meta-analysis to summarise the associations between prenatal or childhood exposure to PFASs and childhood overweight/obesity.

Methods: The search was performed on the bibliographic databases PubMed and Embase with text strings containing terms related to prenatal, breastfeeding, childhood, overweight, obesity, and PFASs. Only papers describing a biomonitoring study in pregnant women or in children up to 18 years that assessed body mass index (BMI), waist circumference (WC), or fat mass in children were included. When the estimates of the association between a PFAS and an outcome were reported from at least 3 studies, a meta-analysis was conducted; moreover, to correctly compare the studies, we developed a method to convert the different effect estimates and made them comparable each other. Meta-analyses were performed also stratifying by sex and age, and sensitivity analyses were also performed.

Results: In total, 484 and 779 articles were retrieved from PubMed and Embase, respectively, resulting in a total of 826 articles after merging duplicates. The papers included in this systematic review were 49: 26 evaluating prenatal exposure to PFASs, 17 childhood exposure, and 6 both. Considering a qualitative evaluation, results were conflicting, with positive, negative, and null associations. 30 papers were included in meta-analyses (19 prenatal, 7 children, and 4 both). Positive associations were evidenced between prenatal PFNA and BMI, between PFOA and BMI in children who were more than 3 years, and between prenatal PFNA and WC. Negative associations were found between prenatal PFOS and BMI in children who were 3 or less years, and between PFHxS and risk of overweight. Relatively more consistent negative associations were evidenced between childhood exposure to three PFASs (PFOA, PFOS, and PFNA) and BMI, in particular PFOS in boys. However, heterogeneity among studies was high.

Conclusion: Even though heterogeneous across studies, the pooled evidence suggests possible associations, mostly positive, between prenatal exposure to some PFASs and childhood BMI/WC; and relatively stronger evidence for negative associations between childhood exposure to PFASs and childhood BMI.

Keywords: Childhood adiposity; Early life exposure; Effect estimate conversion; Fetal exposure; Paediatric exposure; Perfluoroalkyl substances.

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Conflict of interest statement

The authors declare no competing interests.

Figures

Fig. 1
Fig. 1
Summary of the literature search performed in this review
Fig. 2
Fig. 2
Superimposed forest plots of the meta-analyses performed with the inverse variance method considering separately both sexes, boys, and girls. The beta estimates represent the association between the increase of 1 z-score (of BMI or WC) per 1 ng/mL increase in the PFAS. For risk of overweight, the estimates represent transformed standardized mean differences (see section " 2.3.3 Data conversion of the effect estimates"). The squares are proportional to the weight assigned to each study in the random effects models, while horizontal lines represent the 95% confidence intervals reported. The diamonds at the bottom represent the pooled estimated of the random effects models (with the 95% confidence interval). The I2 is also reported as a measure of heterogeneity
Fig. 2
Fig. 2
Superimposed forest plots of the meta-analyses performed with the inverse variance method considering separately both sexes, boys, and girls. The beta estimates represent the association between the increase of 1 z-score (of BMI or WC) per 1 ng/mL increase in the PFAS. For risk of overweight, the estimates represent transformed standardized mean differences (see section " 2.3.3 Data conversion of the effect estimates"). The squares are proportional to the weight assigned to each study in the random effects models, while horizontal lines represent the 95% confidence intervals reported. The diamonds at the bottom represent the pooled estimated of the random effects models (with the 95% confidence interval). The I2 is also reported as a measure of heterogeneity
Fig. 2
Fig. 2
Superimposed forest plots of the meta-analyses performed with the inverse variance method considering separately both sexes, boys, and girls. The beta estimates represent the association between the increase of 1 z-score (of BMI or WC) per 1 ng/mL increase in the PFAS. For risk of overweight, the estimates represent transformed standardized mean differences (see section " 2.3.3 Data conversion of the effect estimates"). The squares are proportional to the weight assigned to each study in the random effects models, while horizontal lines represent the 95% confidence intervals reported. The diamonds at the bottom represent the pooled estimated of the random effects models (with the 95% confidence interval). The I2 is also reported as a measure of heterogeneity

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