Exposure to Per- and Polyfluoroalkyl Substances and Mortality in U.S. Adults: A Population-Based Cohort Study

Background: Per- and polyfluoroalkyl substances (PFAS) are widespread environmental contaminants associated with diseases such as cancer and dyslipidemia. However, few studies have investigated the association between PFAS mixture exposure and mortality in general populations. Objectives: This study aimed to explore the association between PFAS mixture, perfluorooctanoic acid (PFOA), and perfluorooctane sulfonic acid (PFOS) and mortality in U.S. adults by a nationally representative cohort. Methods: Adults ≥18 years of age who were enrolled in the National Health and Nutrition Examination Survey (NHANES) (1999–2014) were included in our study. Baseline serum concentrations of seven PFAS were measured and individuals were followed up to 31 December 2015. Hazard ratios (HRs) and confidence intervals (CIs) were estimated using Cox proportional hazards models. Association between PFAS mixture exposure and mortality was analyzed using the k-means method by clustering PFAS mixtures into subgroups. Association between PFOA/PFOS exposure and mortality was subsequently analyzed in both continuous and categorical models. Results: During the follow-up period, 1,251 participants died. In the mixture analysis, the k-means algorithm clustered participants into low-, medium-, and high-exposure groups. Compared with the low-exposure group, participants in the high-exposure group showed significantly higher risks for all-cause mortality (HR=1.38; 95% CI: 1.07, 1.80), heart disease mortality (HR=1.58; 95% CI: 1.05, 2.51), and cancer mortality (HR=1.70; 95% CI: 1.08, 2.84). In single PFAS analysis, PFOS was found to be positively associated with all-cause mortality (third vs. first tertile HR=1.57; 95% CI: 1.22, 2.07), heart disease mortality (third vs. first tertile HR=1.65; 95% CI: 1.09, 2.57), and cancer mortality (third vs. first tertile HR=1.75; 95% CI: 1.10, 2.83), whereas PFOA exposure had no significant association with mortality. Assuming the observed association is causal, the number of deaths associated with PFOS exposure (≥17.1 vs. <7.9 ng/mL) was ∼382,000 (95% CI: 176,000, 588,000) annually between 1999 and 2015, and it decreased to 69,000 (95% CI: 28,000, 119,000) annually between 2015 and 2018. The association between PFOS and mortality was stronger among women and people without diabetes. Discussion: We observed a positive association between PFAS mixture exposure and mortality among U.S. adults. Limitations of this study include the potential for unmeasured confounding, selection bias, a relatively small number of deaths, and only measuring PFAS at one point in time. Further studies with serial measures of PFAS concentrations and longer follow-ups are necessary to elucidate the association between PFAS and mortality from specific causes. https://doi.org/10.1289/EHP10393

[1]  Leilei Tang,et al.  Perfluorooctane sulfonate induces heart toxicity involving cardiac apoptosis and inflammation in rats , 2021, Experimental and therapeutic medicine.

[2]  Xuewen Xu,et al.  Cadmium exposure in US adults, research based on the National Health and Nutrition Examination Survey from 1988 to 2018 , 2021, Environmental Science and Pollution Research.

[3]  Juntao Wang,et al.  Perfluorooctane sulfonate (PFOS) triggers migration and invasion of esophageal squamous cell carcinoma cells via regulation of Zeb1 , 2021, Drug and chemical toxicology.

[4]  S. Sathyanarayana,et al.  Per- and Polyfluoroalkyl Substances (PFAS) in Breast Milk: Concerning Trends for Current-Use PFAS. , 2021, Environmental science & technology.

[5]  K. Kleinman,et al.  Per- and polyfluoroalkyl substances and calcifications of the coronary and aortic arteries in adults with prediabetes: Results from the diabetes prevention program outcomes study , 2021, Environment international.

[6]  Jun Zhang,et al.  Perfluoroalkyl substances and sex hormones in postmenopausal women: NHANES 2013-2016. , 2021, Environment international.

[7]  K. Mokra,et al.  Endocrine Disruptor Potential of Short- and Long-Chain Perfluoroalkyl Substances (PFASs)—A Synthesis of Current Knowledge with Proposal of Molecular Mechanism , 2021, International journal of molecular sciences.

[8]  A. Furberg,et al.  Exposure to perfluoroalkyl substances (PFAS) and dyslipidemia, hypertension and obesity in adolescents. The Fit Futures study. , 2021, Environmental research.

[9]  R. Naidu,et al.  Exposure to perfluorooctanesulfonate (PFOS) but not perflurorooctanoic acid (PFOA) at ppb concentration induces chronic toxicity in Daphnia carinata. , 2021, The Science of the total environment.

[10]  K. Steenland,et al.  PFAS and cancer, a scoping review of the epidemiologic evidence. , 2020, Environmental research.

[11]  J. Ng,et al.  Assessing the human health risks of per- and polyfluoroalkyl substances: A need for greater focus on their interactions as mixtures. , 2020, Journal of hazardous materials.

[12]  J. Ralston,et al.  Use of Latent Class Analysis and k-Means Clustering to Identify Complex Patient Profiles , 2020, JAMA network open.

[13]  Jianjie Fu,et al.  Evaluation of the Estrogenic/Antiestrogenic Activities of Perfluoroalkyl Substances and Their Interactions with the Human Estrogen Receptor by Combining In Vitro Assays and In Silico Modeling. , 2020, Environmental science & technology.

[14]  Ying Liu,et al.  A Cross-Sectional Study of the Association between Perfluorinated Chemical Exposure and Cancers related to Deregulation of Estrogen Receptors. , 2020, Environmental research.

[15]  Carla A. Ng,et al.  Per‐ and Polyfluoroalkyl Substance Toxicity and Human Health Review: Current State of Knowledge and Strategies for Informing Future Research , 2020, Environmental toxicology and chemistry.

[16]  D. Savitz,et al.  Review: Evolution of evidence on PFOA and health following the assessments of the C8 Science Panel. , 2020, Environment international.

[17]  R. Fry,et al.  Perfluoroalkyl Substances (PFAS) and Their Effects on the Placenta, Pregnancy, and Child Development: a Potential Mechanistic Role for Placental Peroxisome Proliferator–Activated Receptors (PPARs) , 2020, Current Environmental Health Reports.

[18]  Xuelian Bai,et al.  Perfluoroalkyl substances (PFAS) in surface water and sediments from two urban watersheds in Nevada, USA. , 2020, The Science of the total environment.

[19]  M. Longnecker,et al.  The concentration of several perfluoroalkyl acids in serum appears to be reduced by dietary fiber , 2020, medRxiv.

[20]  Chiun-Sheng Huang,et al.  A case-control study of perfluoroalkyl substances and the risk of breast cancer in Taiwanese women. , 2020, Environment international.

[21]  Oliver A.H. Jones,et al.  What are the effects of PFAS exposure at environmentally relevant concentrations? , 2020, Chemosphere.

[22]  M. Brusseau,et al.  PFAS concentrations in soils: Background levels versus contaminated sites. , 2020, The Science of the total environment.

[23]  Zhanyun Wang,et al.  Strategies for grouping per- and polyfluoroalkyl substances (PFAS) to protect human and environmental health. , 2020, Environmental science. Processes & impacts.

[24]  S. Harlow,et al.  Perfluoroalkyl and polyfluoroalkyl substances (PFAS) and their effects on the ovary , 2020, Human reproduction update.

[25]  Jun Zhang,et al.  Perfluoroalkyl and polyfluroalkyl substances and maternal thyroid hormones in early pregnancy. , 2020, Environmental pollution.

[26]  A. Braeuning,et al.  Activation of human nuclear receptors by perfluoroalkylated substances (PFAS). , 2020, Toxicology in vitro : an international journal published in association with BIBRA.

[27]  P. Girardi,et al.  A mortality study on male subjects exposed to polyfluoroalkyl acids with high internal dose of perfluorooctanoic acid. , 2019, Environmental research.

[28]  Jun Zhang,et al.  Characteristic and human exposure risk assessment of per- and polyfluoroalkyl substances: A study based on indoor dust and drinking water in China. , 2019, Environmental pollution.

[29]  M. Nadal,et al.  Human exposure to per- and polyfluoroalkyl substances (PFAS) through drinking water: A review of the recent scientific literature. , 2019, Environmental research.

[30]  Katherine E Pelch,et al.  PFAS health effects database: Protocol for a systematic evidence map. , 2019, Environment international.

[31]  K. Kleinman,et al.  Per- and polyfluoroalkyl substances and blood lipid levels in pre-diabetic adults-longitudinal analysis of the diabetes prevention program outcomes study. , 2019, Environment international.

[32]  June-Woo Park,et al.  Perfluorooctanoic acid (PFOA) and perfluooctane sulfonate (PFOS) induce different modes of action in reproduction to Japanese medaka (Oryzias latipes). , 2019, Journal of hazardous materials.

[33]  Hong Jiang,et al.  PFOS, PFOA, estrogen homeostasis, and birth size in Chinese infants. , 2019, Chemosphere.

[34]  S. Kirkpatrick,et al.  Applications of the Healthy Eating Index for Surveillance, Epidemiology, and Intervention Research: Considerations and Caveats. , 2018, Journal of the Academy of Nutrition and Dietetics.

[35]  D. Ray,et al.  Molecular Actions of PPARα in Lipid Metabolism and Inflammation. , 2018, Endocrine reviews.

[36]  A. Screpanti,et al.  Drinking water contamination from perfluoroalkyl substances (PFAS): an ecological mortality study in the Veneto Region, Italy , 2018, European journal of public health.

[37]  E. Testai,et al.  Biomonitoring of perfluorinated compounds in adults exposed to contaminated drinking water in the Veneto Region, Italy. , 2018, Environment international.

[38]  Osmar R Zaiane,et al.  A systematic review of data mining and machine learning for air pollution epidemiology , 2017, BMC Public Health.

[39]  Paula Pierozan,et al.  PFOS induces proliferation, cell-cycle progression, and malignant phenotype in human breast epithelial cells , 2017, Archives of Toxicology.

[40]  Y. Li,et al.  Half-lives of PFOS, PFHxS and PFOA after end of exposure to contaminated drinking water , 2017, Occupational and Environmental Medicine.

[41]  J. Olgin,et al.  Volunteer Participation in the Health eHeart Study: A Comparison with the US Population , 2017, Scientific Reports.

[42]  F. Santini,et al.  Thyroid disruption by perfluorooctane sulfonate (PFOS) and perfluorooctanoate (PFOA) , 2017, Journal of Endocrinological Investigation.

[43]  K. Flegal,et al.  Trends in Obesity Among Adults in the United States, 2005 to 2014. , 2016, JAMA.

[44]  S. Bugel,et al.  PFOS, PFNA, and PFOA sub-lethal exposure to embryonic zebrafish have different toxicity profiles in terms of morphometrics, behavior and gene expression. , 2016, Aquatic toxicology.

[45]  Tony Fletcher,et al.  The C8 Health Project: Design, Methods, and Participants , 2009, Environmental health perspectives.

[46]  D. Spiegelman,et al.  Point and interval estimates of partial population attributable risks in cohort studies: examples and software , 2007, Cancer Causes & Control.

[47]  L E Daly,et al.  Confidence limits made easy: interval estimation using a substitution method. , 1998, American journal of epidemiology.

[48]  David A. Schoenfeld,et al.  Partial residuals for the proportional hazards regression model , 1982 .

[49]  S. Walter The distribution of Levin's measure of attributable risk , 1975 .

[50]  M. Levin,et al.  The occurrence of lung cancer in man. , 1953, Acta - Unio Internationalis Contra Cancrum.