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. 2022 Sep;212(Pt B):113296.
doi: 10.1016/j.envres.2022.113296. Epub 2022 Apr 18.

Plasma concentrations of lipophilic persistent organic pollutants and glucose homeostasis in youth populations

Affiliations

Plasma concentrations of lipophilic persistent organic pollutants and glucose homeostasis in youth populations

Brittney O Baumert et al. Environ Res. 2022 Sep.

Abstract

Background: Exposure to lipophilic persistent organic pollutants (POPs) is ubiquitous. POPs are metabolic disrupting chemicals and are potentially diabetogenic.

Methods: Using a multi-cohort study including overweight adolescents from the Study of Latino Adolescents at Risk (SOLAR, N = 301, 2001-2012) and young adults from the Southern California Children's Health Study (CHS, N = 135, 2014-2018), we examined associations of POPs and risk factors for type 2 diabetes. SOLAR participants underwent annual visits for a median of 2.2 years and CHS participants performed a single visit, during which a 2-h oral glucose tolerance test was performed. Linear mixed models were used to examine associations between plasma concentrations of POPs [4,4'-dichlorodiphenyldichloroethylene (4,4'-DDE), hexachlorobenzene (HCB), PCBs-153, 138, 118, 180 and PBDEs-154, 153, 100, 85, 47] and changes in glucose homeostasis across age and pubertal stage.

Results: In SOLAR, exposure to HCB, PCB-118, and PBDE-153 was associated with dysregulated glucose metabolism. For example, each two-fold increase in HCB was associated with approximately 2 mg/dL higher glucose concentrations at 30 min (p = 0.001), 45 min (p = 0.0006), and 60 min (p = 0.03) post glucose challenge. Compared to individuals with low levels of PCB-118, individuals with high levels exhibited a 4.7 mg/dL (p = 0.02) higher glucose concentration at 15 min and a 3.6 mg/dL (p = 0.01) higher glucose concentration at 30 min. The effects observed with exposure to organochlorine compounds were independent of pubertal stages. PBDE-153 was associated with the development of dysregulated glucose metabolism beginning in late puberty. At Tanner stage 4, exposure to PBDE-153 was associated with a 12.7 mg/dL higher 60-min glucose concentration (p = 0.009) and a 16.1 mg*dl-1*hr-1 higher glucose AUC (p = 0.01). These associations persisted at Tanner 5. In CHS, PBDE-153 and total PBDE were associated with similar increases in glucose concentrations.

Conclusion: Our results suggest that childhood exposure to lipophilic POPs is associated with dysregulated glucose metabolism.

Keywords: Flame retardants; Obesogens; Organochlorines; Pesticides; Polybrominated compounds; Type II diabetes.

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Conflict of interest statement

Conflict of interest disclosures.

The authors declare that they have no conflicts of interest.

Declaration of competing financial interests.

The authors declare they have no actual or potential competing financial interests.

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.

Figures

Figure 1.
Figure 1.
Correlation of lipophilic compounds in the SOLAR and CHS cohorts. Correlations between two continuous variables were calculated using the Pearson correlation coefficient; correlations between two binary variables were calculated with polychoric correlation coefficients; and correlations between a continuous and binomial variable were calculated with polyserial correlation coefficients. * indicates chemicals detected in less than 75% of samples and which were analyzed as binary (detect/non-detect); ** indicates correlations which were statistically significant based upon a p<0.05.
Figure 2.
Figure 2.
Point estimates and 95% confidence intervals for associations of (A) Hexachlorobenzene (HCB); (B) polybrominated diphenyl ether (PBDE)-153, and (C) Total PBDEs with risk factors for type 2 diabetes in SOLAR and CHS. Associations of HCB with glucose concentrations during the Oral Glucose Tolerance Test were not time dependent, so panel A represents the change in glucose concentration and glucose AUC per doubling of HCB across all developmental stages for SOLAR. Panels B and C represents the difference in outcome for (B) detected vs. non-detected levels of PBDE-153 and (C) the 80th vs. 20th percentile of total PBDE exposure across developmental stages. * indicates chemicals detected in less than 75% of samples and which were analyzed as binary (detect/non-detect). Notes: OGTT Time point 0 corresponds to fasting glucose; Glu: Glucose; AUC: Area under the curve; ISI Matsuda: Matsuda Insulin Sensitivity Index.
Figure 3.
Figure 3.
Associations of a mixture of eleven lipophilic POPs with glucose responses to an oral glucose tolerance test in adolescents in late puberty (SOLAR) and young adults (CHS). Effect estimates (ψ) and 95% confidence intervals indicate the change in glucose levels (A) or glucose area under the curve (B) when increasing all lipophilic POPs levels from low to high. For POPs detected in >75% of participants, low vs. high levels were determined by the median; for POPs levels detected in <75% of participants, low vs. high levels were defined as detected versus non-detected. Glu: Glucose; AUC: Area under the curve.

References

    1. Airaksinen R, et al., 2011. Association between type 2 diabetes and exposure to persistent organic pollutants. Diabetes Care. 34, 1972–9. - PMC - PubMed
    1. Alderete TL, et al., 2017. Longitudinal Associations Between Ambient Air Pollution With Insulin Sensitivity, beta-Cell Function, and Adiposity in Los Angeles Latino Children. Diabetes. 66, 1789–1796. - PMC - PubMed
    1. Beard J, et al., 2003. Health impacts of pesticide exposure in a cohort of outdoor workers. Environ Health Perspect. 111, 724–30. - PMC - PubMed
    1. Benjamini Y, Hochberg Y, 1995. Controlling the False Discovery Rate: A Practical and Powerful Approach to Multiple Testing. Journal of the Royal Statistical Society. Series B (Methodological). 57, 289–300.
    1. Costa LG, et al., 2014. A mechanistic view of polybrominated diphenyl ether (PBDE) developmental neurotoxicity. Toxicol Lett. 230, 282–94. - PMC - PubMed

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