Serum Perfluoroalkyl Acids Concentrations and Memory

Total Page:16

File Type:pdf, Size:1020Kb

Serum Perfluoroalkyl Acids Concentrations and Memory Open Access Research BMJ Open: first published as 10.1136/bmjopen-2012-002414 on 6 June 2013. Downloaded from Serum perfluoroalkyl acids concentrations and memory impairment in a large cross-sectional study Valentina Gallo,1,2 Giovanni Leonardi,1 Carol Brayne,3 Ben Armstrong,1 Tony Fletcher1 To cite: Gallo V, Leonardi G, ABSTRACT et al ARTICLE SUMMARY Brayne C, . Serum Objectives: To examine the cross-sectional perfluoroalkyl acids association between serum perfluorooctanate (PFOA), concentrations and memory Article focus perfuorooctane sulfonate (PFOS), perfluorononanoic impairment in a large cross- ▪ Cross-sectional association between the serum sectional study. BMJ Open acid (PFNA) and perfluorohexane sulfonate (PFHxS) level of perfluorooctanate (PFOA), perfluoro-octane 2013;3:e002414. concentrations with self-reported memory impairment sulfonate (PFOS), perfluorononanoic acid (PFNA) doi:10.1136/bmjopen-2012- in adults and the interaction of these associations with and perfluorohexane sulfonate (PFHxS) and self- 002414 diabetes status. reported memory impairment in a population Design: Cross-sectional study. exposed to high levels of PFOA. ▸ Prepublication history and Setting: Population-based in Mid-Ohio Valley, West ▪ Potential interaction between the association of additional material for this Virginia following contamination by a chemical plant. perfluoroalkyl acids (PFAAs) with memory paper is available online. To Participants: The C8 Health Project collected data impairment by diabetes status. view these files please visit and measured the serum level of perfluoroalkyl acids the journal online (PFAAs) of 21 024 adults aged 50+ years. Key messages (http://dx.doi.org/10.1136/ ▪ Inverse associations between PFOS and PFOA Primary outcome measure: Self-reported memory bmjopen-2012-002414). and memory impairment were statistically signifi- impairment as defined by the question ‘have cant, perhaps due to a potential anti- experienced short-term memory loss?’ Received 27 November 2012 inflammatory effect exerted through a peroxi- Revised 30 April 2013 Results: A total of 4057 participants self-reported some proliferator-activated receptor agonism. Accepted 30 April 2013 http://bmjopen.bmj.com/ short-term memory impairment. Inverse associations Comparable inverse associations with PFNA and between PFOS and PFOA and memory impairment PFHxS were of borderline statistical significance. were highly statistically significant with fully adjusted ▪ Inverse associations of PFAAs with memory This final article is available OR=0.93 (95% CI 0.90 to 0.96) for doubling PFOS for use under the terms of impairment were weaker or non-existent in and OR=0.96 (95% CI 0.94 to 0.98) for doubling PFOA the Creative Commons patients with diabetes than overall in patients Attribution Non-Commercial concentrations. Comparable inverse associations with without diabetes. Analysis further stratified by 2.0 Licence; see PFNA and PFHxS were of borderline statistical specific diabetes medication use showed no vari- http://bmjopen.bmj.com significance. Inverse associations of PFAAs with ation in ORs more than explicable by chance memory impairment were weaker or non-existent in given the number of tests made. on September 25, 2021 by guest. Protected copyright. patients with diabetes than overall in patients without diabetes. Strengths and limitations of this study Conclusions: An inverse association between PFAA ▪ Very large sample size including 21 024 adults serum levels and self-reported memory impairment has with a measured serum level of PFAAs with a been observed in this large population-based, cross- given geographical distribution allowing some 1Department of Social and Environmental Health sectional study that is stronger and more statistically multilevel modelling. ▪ Research, London School of significant for PFOA and PFOS. The associations can The cross-sectional nature of the design does Hygiene and Tropical be potentially explained by a preventive anti- not allow any causal inference and makes results Medicine, London, UK inflammatory effect exerted by a peroxisome particularly prone to reverse causality. 2Centre for Primary Care and proliferator-activated receptor agonist effect of these ▪ A self-report is not an optimal method for Public Health, Blizard PFAAs, but confounding or even reverse causation estimating the degree of memory impairment in Institute, Queen Mary, cannot be excluded as an alternative explanation. a population. University of London, London, UK 3Department of Public Health and Primary Care, University and breathable, yet waterproof, fabrics. of Cambridge, Cambridge, They can also result from the metabolism of UK INTRODUCTION fluorinated telomers, compounds used fl Correspondence to Per uoroalkyl acids (PFAAs) are man-made for food package coatings, carpet treatments Dr Valentina Gallo; compounds used during the manufacture of and stain-resistant fabric treatment. [email protected] fluoropolymers including non-stick cookware Perfluorooctanate (PFOA), perfuorooctane Gallo V, Leonardi G, Brayne C, et al. BMJ Open 2013;3:e002414. doi:10.1136/bmjopen-2012-002414 1 Perfluoroalkyl acids and memory impairment BMJ Open: first published as 10.1136/bmjopen-2012-002414 on 6 June 2013. Downloaded from sulfonate (PFOS), perfluorononanoic acid (PFNA) and that gathered data from over 69 000 people from six perfluorohexane sulfonate (PFHxS) persist in the envir- contaminated water districts surrounding the plant.25 In onment and are found in the blood of humans and the present population, PFOA concentrations ranged many animal species throughout the world.12Potential from US background levels to very high; overall, the sources of exposure to PFAAs in humans include drink- PFOA levels are much higher in this population (geo- ing water, dust, breast milk, fish and other foods, food metric mean 42.6 ng/ml, 95% CI 41.8 to 43.3) than in – packaging, ambient air, and occupational exposure.3 6 the corresponding US population surveys (NHANES in In animal models, perfluoroalkyl chemicals can acti- same year mean 3.95 ng/ml, 95% CI 3.65 to 4.27).125 vate peroxisome proliferator-activated receptor α The mean PFOS (geometric mean 22.4, 95% CI 22.2 to (PPARα), a ligand-activated transcription factor that reg- 22.6), PFNA (1.37, 95% CI 1.36 to 1.38) and PFHXs ulates gene expression, lipid modulation, glucose (3.18, 95% CI 3.15 to 3.22) closely resembled values homeostasis, cell proliferation and inflammation.78The from a nationally representative US sample from a PPAR receptor has been involved in the ageing process: similar time frame (mean PFOS 20.7, 95% CI 19.2 to PPARα null mice showed decreased longevity compared 22.3; mean PFNA 0.97, 95% CI 0.82 to 1.14 and PFHXs with wild-type mice due to non-neoplastic spontaneous 1.93, 95% CI 1.73 to 2.16).1 ageing lesions which occurred with a higher incidence The present study uses these data to examine the and a shorter latency in the PPARα null mice.9 Also, cross-sectional association between serum PFOA, PFOS, PPARγ variants were reported to be associated with lon- PFNA and PFHxS concentrations with self-reported gevity in humans with low-insulin resistance.10 11 memory impairment in adults, and its potential inter- Activation of the PPARγ receptor in vitro and in vivo action with diabetes status. also prevents the expression of inflammatory cytokines and other inflammatory mediators in brains of Alzheimer’s disease animal models.12 13 In addition, PPARγ agonists have been demonstrated to suppress the METHODS Aβ-mediated activation of microglia in vitro and prevent Study population – cortical or hippocampal neuronal cell death.14 16 PPARγ This study is one of the C8 Science Panel Studies that is also deeply involved in diabetes, given its ability to uses information from questionnaires and blood tests orchestrate the expression of genes involved in lipid collected in the C8 Health Project, supplemented by metabolism, adipogenesis and inflammation. It is acti- further information on classification by water district vated by endogenous ligands (such as fatty acids and developed in a companion C8 Science Panel Study. prostaglandins) or drugs such as thiazolidinedione. It is The C8 Health Project enrolled eligible participants http://bmjopen.bmj.com/ most highly expressed in adipocytes where it acts as the between August 2005 and August 2006. Individuals were master regulator of adipogenesis via induction of adipo- eligible to participate in the C8 Health Project if they genic genes.17 However, a study in vitro showed that had consumed water for at least 1 year between 1950 PFOA and PFOS activate differentially PPARα and and 3 December 2004 while living, working or going to PPARγ receptors, but it is not possible to directly school in one of the following six water districts: Little extrapolate these results to toxicity studies in vivo.18 Hocking Water Association of Ohio; City of Belpre, Therefore, in line with what was recently observed by Ohio; Tupper Plains-Chester District of Ohio; Village of Power et al,19 we hypothesised that increased exposure to Pomeroy, Ohio; Lubeck Public Service District of West on September 25, 2021 by guest. Protected copyright. PFAA could be associated with a better cognitive Virginia; Mason County Public Service District of West function. Virginia or private water sources within aforementioned The positive association between diabetes and cogni- districts and areas of documented PFOA contamination. tive impairment is well established20; some studies inves- Details of the study enrolment
Recommended publications
  • Chemicals in the Fourth Report and Updated Tables Pdf Icon[PDF
    Chemicals in the Fourth National Report on Human Exposure to Environmental Chemicals: Updated Tables, March 2021 CDC’s Fourth National Report on Human Exposure to Environmental Chemicals: Updated Tables, March 2021 provides exposure data on the following chemicals or classes of chemicals. The Updated Tables contain cumulative data from national samples collected beginning in 1999–2000 and as recently as 2015-2016. Not all chemicals were measured in each national sample. The data tables are available at https://www.cdc.gov/exposurereport. An asterisk (*) indicates the chemical has been added since publication of the Fourth National Report on Human Exposure to Environmental Chemicals in 2009. Adducts of Hemoglobin Acrylamide Formaldehyde* Glycidamide Tobacco Alkaloids and Metabolites Anabasine* Anatabine* Cotinine Cotinine-n-oxide* Hydroxycotinine* Trans-3’-hydroxycotinine* 1-(3-Pyridyl)-1-butanol-4-carboxylic acid* Nicotine* Nicotine-N’-oxide* Nornicotine* Tobacco-Specific Nitrosamines (TSNAs) N’-Nitrosoanabasine (NAB)* N’-Nitrosoanatabine (NAT)* N’-Nitrosonornicotine (NNN)* Total 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanol) (NNAL)* Volatile N-nitrosamines (VNAs) N-Nitrosodiethylamine (NDEA)* N-Nitrosoethylmethylamine (NMEA)* N-Nitrosomorpholine (NMOR)* N-Nitrosopiperidine (NPIP)* N-Nitrosopyrrolidine (NPYR)* Disinfection By-Products Bromodichloromethane Dibromochloromethane Tribromomethane (Bromoform) Trichloromethane (Chloroform) Personal Care and Consumer Product Chemicals and Metabolites Benzophenone-3 Bisphenol A Bisphenol F* Bisphenol
    [Show full text]
  • Pfoa) Or Perfluorooctane Sulfonate (Pfos
    National Toxicology Program NTP U.S. Department of Health and Human Services NTP Monograph Immunotoxicity Associated with Exposure to Perfluorooctanoic Acid or Perfluorooctane Sulfonate September 2016 NTP MONOGRAPH ON IMMUNOTOXICITY ASSOCIATED WITH EXPOSURE TO PERFLUOROOCTANOIC ACID (PFOA) OR PERFLUOROOCTANE SULFONATE (PFOS) September, 2016 Office of Health Assessment and Translation Division of the National Toxicology Program National Institute of Environmental Health Sciences National Institutes of Health U.S. DEPARTMENT OF HEALTH AND HUMAN SERVICES Systematic Review of Immunotoxicity Associated with Exposure to PFOA or PFOS TABLE OF CONTENTS Table of Contents ...............................................................................................................................II List of Table and Figures ................................................................................................................... IV Abstract ............................................................................................................................................. 1 Peer Review Of The Draft NTP Monograph ......................................................................................... 2 Peer-Review Panel .............................................................................................................................. 2 Introduction ...................................................................................................................................... 3 Objective and Specific Aims ...............................................................................................................
    [Show full text]
  • PFAS MCL Technical Support Document
    ATTACHMENT 1 New Hampshire Department of Environmental Services Technical Background Report for the June 2019 Proposed Maximum Contaminant Levels (MCLs) and Ambient Groundwater Quality Standards (AGQSs) for Perfluorooctane sulfonic Acid (PFOS), Perfluorooctanoic Acid (PFOA), Perfluorononanoic Acid (PFNA), and Perfluorohexane sulfonic Acid (PFHxS) And Letter from Dr. Stephen M. Roberts, Ph.D. dated 6/25/2019 – Findings of Peer Review Conducted on Technical Background Report June 28, 2019 New Hampshire Department of Environmental Services Technical Background Report for the June 2019 Proposed Maximum Contaminant Levels (MCLs) and Ambient Groundwater Quality Standards (AGQSs) for Perfluorooctane sulfonic Acid (PFOS), Perfluorooctanoic Acid (PFOA), Perfluorononanoic Acid (PFNA), and Perfluorohexane sulfonic Acid (PFHxS) June 28, 2019 Table of Contents Abbreviations ................................................................................................................................................. i Acknowledgements ...................................................................................................................................... iii Section I. Executive Summary ....................................................................................................................... 1 Section II. Introduction ................................................................................................................................. 2 Section III. Reference Dose Derivation ........................................................................................................
    [Show full text]
  • Health Effects Support Document for Perfluorooctanoic Acid (PFOA)
    United States Office of Water EPA 822-R-16-003 Environmental Protection Mail Code 4304T May 2016 Agency Health Effects Support Document for Perfluorooctanoic Acid (PFOA) Perfluorooctanoic Acid – May 2016 i Health Effects Support Document for Perfluorooctanoic Acid (PFOA) U.S. Environmental Protection Agency Office of Water (4304T) Health and Ecological Criteria Division Washington, DC 20460 EPA Document Number: 822-R-16-003 May 2016 Perfluorooctanoic Acid – May 2016 ii BACKGROUND The Safe Drinking Water Act (SDWA), as amended in 1996, requires the Administrator of the U.S. Environmental Protection Agency (EPA) to periodically publish a list of unregulated chemical contaminants known or anticipated to occur in public water systems and that may require regulation under SDWA. The SDWA also requires the Agency to make regulatory determinations on at least five contaminants on the Contaminant Candidate List (CCL) every 5 years. For each contaminant on the CCL, before EPA makes a regulatory determination, the Agency needs to obtain sufficient data to conduct analyses on the extent to which the contaminant occurs and the risk it poses to populations via drinking water. Ultimately, this information will assist the Agency in determining the most appropriate course of action in relation to the contaminant (e.g., developing a regulation to control it in drinking water, developing guidance, or deciding not to regulate it). The PFOA health assessment was initiated by the Office of Water, Office of Science and Technology in 2009. The draft Health Effects Support Document for Perfluoroctanoic Acid (PFOA) was completed in 2013 and released for public comment in February 2014.
    [Show full text]
  • Perfluorooctane Sulfonate (PFOS) and Perfluorooctanoic Acid (PFOA) November 2017 TECHNICAL FACT SHEET – PFOS and PFOA
    Technical Fact Sheet – Perfluorooctane Sulfonate (PFOS) and Perfluorooctanoic Acid (PFOA) November 2017 TECHNICAL FACT SHEET – PFOS and PFOA Introduction At a Glance This fact sheet, developed by the U.S. Environmental Protection Agency Manmade chemicals not (EPA) Federal Facilities Restoration and Reuse Office (FFRRO), provides a naturally found in the summary of two contaminants of emerging concern, perfluorooctane environment. sulfonate (PFOS) and perfluorooctanoic acid (PFOA), including physical and Fluorinated compounds that chemical properties; environmental and health impacts; existing federal and repel oil and water. state guidelines; detection and treatment methods; and additional sources of information. This fact sheet is intended for use by site managers who may Used in a variety of industrial address these chemicals at cleanup sites or in drinking water supplies and and consumer products, such for those in a position to consider whether these chemicals should be added as carpet and clothing to the analytical suite for site investigations. treatments and firefighting foams. PFOS and PFOA are part of a larger group of chemicals called per- and Extremely persistent in the polyfluoroalkyl substances (PFASs). PFASs, which are highly fluorinated environment. aliphatic molecules, have been released to the environment through Known to bioaccumulate in industrial manufacturing and through use and disposal of PFAS-containing humans and wildlife. products (Liu and Mejia Avendano 2013). PFOS and PFOA are the most Readily absorbed after oral widely studied of the PFAS chemicals. PFOS and PFOA are persistent in the exposure. Accumulate environment and resistant to typical environmental degradation processes. primarily in the blood serum, As a result, they are widely distributed across all trophic levels and are found kidney and liver.
    [Show full text]
  • Microbiota and Obesogens: Environmental Regulators of Fat Storage
    Microbiota and obesogens: environmental regulators of fat storage John F. Rawls, Ph.D. Department of Molecular Genetics & Microbiology Center for Genomics of Microbial Systems Duke University School of Medicine Seminar outline 1. Introduction to the microbiota 2. Microbiota as environmental factors in obesity 3. Obesogens as environmental factors in obesity Seeing and understanding the unseen Antonie van Leewenhoek 1620’s: Described differences between microbes associated with teeth & feces during health & disease. Louis Pasteur 1850’s: Helps establish the “germ theory” of disease. 1885: Predicts that germ-free animals can not survive without “common microorganisms”. Culture-independent analysis of bacterial communities using 16S rRNA gene sequencing 16S rRNA 16S SSU rRNA 16S rRNA gene V1 V2 V3 V4 V5 V6 V7 V8 V9 Culture-independent analysis of bacterial communities using 16S rRNA gene sequencing plantbiology.siu.edu Phylogenetic analysis of 16S rRNA genes revealed 3 domains and a vast unappreciated diversity of microbial life You are here Carl Woese Glossary • Microbiota / microflora: the microorganisms of a particular site, habitat, or period of time. • Microbiome: the collective genomes of the microorganisms within a microbiota. • Germ-free / axenic: of a culture that is free from living organisms other than the host species. • Gnotobiotic: of an environment for rearing organisms in which all the microorganisms are either excluded or known. Current techniques for microbiome profiling Microbial community Morgan et al. (2012) Trends in
    [Show full text]
  • Perfluorooctanoic Acid (Pfoa) and Perfluorooctanesulfonic Acid (Pfos)
    WATER QUALITY FACT SHEET: PERFLUOROOCTANOIC ACID (PFOA) AND PERFLUOROOCTANESULFONIC ACID (PFOS) Chemical Properties: • PFOA and PFOS are fluorinated organic chemicals that are part of a larger man-made chemical group referred to as per- and polyfluoroalkyl substances (PFAS), which are resistant to heat, water, and oil. • The chemicals have been used in consumer products such as carpets, clothing, fabrics for furniture, paper packaging for food, and other materials (e.g., cookware) designed to be waterproof, stain- resistant or non-stick. • They also have been used in fire-retarding foam at airfields, military bases, and various industrial processes. • PFOA and PFOS have been the most extensively produced and studied PFAS. PFAS also includes GenX chemicals and perfluorobutane sulfonic acid (PFBS) which require further study. • PFAS tends to accumulate in groundwater with contamination typically localized and associated with facilities where the chemicals were produced or used to manufacture other products. Health Concerns: • In 2016, the United States Environmental Protection Agency (USEPA) issued a lifetime health advisory for PFOA and PFOS for drinking water. Municipalities were advised that they should notify their customers of the presence of levels over 70 ppt (0.07 µg/L) in community water supplies. • Studies indicate that PFOA and PFOS may result in adverse health effects including developmental effects to fetuses during pregnancy or breastfed infants, cancer, liver effects, immune effects, thyroid effects, and cholesterol changes. Regulatory Considerations: • The USEPA has not regulated PFOA and PFOS. There is no Federal MCL or MCLG. • In August 2019, the California State Water Resources Control Board Division of Drinking Water (DDW) updated notification levels for PFOA and PFOS from 14 ppt to 5.1 ppt for PFOA and from 13 ppt to 6.5 ppt for PFOS.
    [Show full text]
  • Perfluorooctanoic Acid Levels, Nuclear Receptor Gene Polymorphisms, And
    www.nature.com/scientificreports OPEN Associations among perfuorooctanesulfonic/ perfuorooctanoic acid levels, nuclear receptor gene polymorphisms, and lipid levels in pregnant women in the Hokkaido study Sumitaka Kobayashi1, Fumihiro Sata1,2, Houman Goudarzi1,3, Atsuko Araki1, Chihiro Miyashita1, Seiko Sasaki4, Emiko Okada5, Yusuke Iwasaki6, Tamie Nakajima7 & Reiko Kishi1* The efect of interactions between perfuorooctanesulfonic (PFOS)/perfuorooctanoic acid (PFOA) levels and nuclear receptor genotypes on fatty acid (FA) levels, including those of triglycerides, is not clear understood. Therefore, in the present study, we aimed to analyse the association of PFOS/PFOA levels and single-nucleotide polymorphisms (SNPs) in nuclear receptors with FA levels in pregnant women. We analysed 504 mothers in a birth cohort between 2002 and 2005 in Japan. Serum PFOS/ PFOA and FA levels were measured using liquid chromatography-tandem mass spectrometry and gas chromatography-mass spectrometry. Maternal genotypes in PPARA (rs1800234; rs135561), PPARG (rs3856806), PPARGC1A (rs2970847; rs8192678), PPARD (rs1053049; rs2267668), CAR (rs2307424; rs2501873), LXRA (rs2279238) and LXRB (rs1405655; rs2303044; rs4802703) were analysed. When gene-environment interaction was considered, PFOS exposure (log10 scale) decreased palmitic, palmitoleic, and oleic acid levels (log10 scale), with the observed β in the range of − 0.452 to − 0.244; PPARGC1A (rs8192678) and PPARD (rs1053049; rs2267668) genotypes decreased triglyceride, palmitic, palmitoleic, and oleic acid levels, with the observed β in the range of − 0.266 to − 0.176. Interactions between PFOS exposure and SNPs were signifcant for palmitic acid (Pint = 0.004 to 0.017). In conclusion, the interactions between maternal PFOS levels and PPARGC1A or PPARD may modify maternal FA levels. Te genetic makeup of a person and the environmental factors might be responsible for regulating the levels of serum lipids, such as fatty acids (FA) and triglycerides (TG)1.
    [Show full text]
  • Environmental Factors, Epigenetics, and Developmental Origin of Reproductive Disorders
    HHS Public Access Author manuscript Author ManuscriptAuthor Manuscript Author Reprod Manuscript Author Toxicol. Author Manuscript Author manuscript; available in PMC 2018 March 01. Published in final edited form as: Reprod Toxicol. 2017 March ; 68: 85–104. doi:10.1016/j.reprotox.2016.07.011. Environmental Factors, Epigenetics, and Developmental Origin of Reproductive Disorders Shuk-Mei Hoa,b,c,d,*, Ana Cheonga,b, Margaret A. Adgente, Jennifer Veeversa,c, Alisa A. Suenf,g, Neville N.C. Tama,b,c, Yuet-Kin Leunga,b,c, Wendy N. Jeffersonf, and Carmen J. Williamsf,* aDepartment of Environmental Health, University of Cincinnati College of Medicine, Cincinnati, Ohio, United States of America bCenter for Environmental Genetics, University of Cincinnati College of Medicine, Cincinnati, Ohio, United States of America cCincinnati Cancer Center, Cincinnati, Ohio, United States of America dCincinnati Veteran Affairs Hospital Medical Center, Cincinnati, Ohio, United States of America eDepartment of Pediatrics, Vanderbilt University Medical Center, Nashville, Tennessee, United States of America fReproductive Medicine Group, Reproductive & Developmental Biology Laboratory, National Institute of Environmental Health Sciences, Research Triangle Park, North Carolina, United States of America gCurriculum in Toxicology, UNC Chapel Hill, Chapel Hill, North Carolina, United States of America Abstract Sex-specific differentiation, development, and function of the reproductive system are largely dependent on steroid hormones. For this reason, developmental exposure
    [Show full text]
  • Perfluorooctanoic Acid (PFOA)
    PERFLUOROOCTANOIC ACID 1. Exposure Data 1.1.2 Structural and molecular formulae, and relative molecular mass: straight-chain 1.1 Identification of the agent isomer 1.1.1 Nomenclature F FFF F F F O F Chem. Abstr. Serv. Reg. No.: 335-67-1 OH Chem. Abstr. Serv. Name: Perfluorooctanoic FFF F F F F acid Molecular formula: C8HF15O2 IUPAC Name: 2,2,3,3,4,4,5,5,6,6,7,7,8,8,8- Relative molecular mass: 414 pentadecafluorooctanoic acid Synonyms: PFOA; pentadecafluoro-1-octan - 1.1.3 Chemical and physical properties of the oic acid; pentadecafluoro-n-octanoic acid; pure substance: straight-chain isomer pentadecaflurooctanoic acid; perfluoro- caprylic acid; perfluoroctanoic acid; From HSDB (2014), unless otherwise perfluoroheptanecarboxylic acid; APFO; indicated ammonium perfluorooctanoate Description: White to off-white powder Isomers and Salts: There are 39 possible struc- Boiling point: 192.4 °C tural isomers of pentadecafluorooctanoic acid (1 with chain length 8, 5 with chain Melting point: 54.3 °C length 7, 13 with chain length 6, 16 with chain Density: 1.792 g/cm3 at 20 °C length 5, and 4 with chain length 4). These Solubility: 9.5 g/L in water at 25 °C isomers can also exist as the ammonium, Vapour pressure: 0.0023 kPa at 20 °C (extrap- sodium, or potassium salt (Nielsen, 2012). olated); 0.127 kPa at 59.25 °C (measured) Fig. 1.1 presents the few isomers and salts (ATSDR, 2009); 0.070 kPa at 25 °C that have Chemical Abstracts Service (CAS) Stability: When heated to decomposition it references.
    [Show full text]
  • Per- and Polyfluoroalkyl Substances Differentially Inhibit Placental Trophoblast Migration and Invasion in Vitro John T
    TOXICOLOGICAL SCIENCES, 2020, 1–10 doi: 10.1093/toxsci/kfaa043 Downloaded from https://academic.oup.com/toxsci/advance-article-abstract/doi/10.1093/toxsci/kfaa043/5812793 by University of North Carolina at Chapel Hill user on 19 May 2020 Advance Access Publication Date: March 27, 2020 Research Article Per- and Polyfluoroalkyl Substances Differentially Inhibit Placental Trophoblast Migration and Invasion In Vitro John T. Szilagyi ,*,† Anastasia N. Freedman,* Stewart L. Kepper,* Arjun M. Keshava,* Jackie T. Bangma,*,‡ and Rebecca C. Fry*,†,‡,1 *Department of Environmental Sciences and Engineering, Gillings School of Global Public Health; †Curriculum in Toxicology; and ‡Institute for Environmental Health Solutions, University of North Carolina, Chapel Hill, North Carolina 27516 1To whom correspondence should be addressed at Department of Environmental Sciences and Engineering, Gillings School of Global Public Health, University of North Carolina, 135 Dauer Drive, CB 7431, Chapel Hill, NC 27516. Fax: (919) 843-9047. E-mail: [email protected]. ABSTRACT Per- and polyfluoroalkyl substances (PFAS) are used as industrial surfactants and chemical coatings for household goods such as Teflon. Despite regulatory efforts to phase out legacy PFAS, they remain detectable in drinking water throughout the United States. This is due to the stability of legacy PFAS and the continued use of replacement compounds. In humans, PFAS have been detected in placenta and cord blood and are associated with low birth weight and preeclampsia risk. Preeclampsia is a leading cause of maternal mortality and is driven by insufficient endometrial trophoblast invasion, resulting in poor placental blood flow. PFAS alter invasion of other cell types, but their impact on trophoblasts is not understood.
    [Show full text]
  • Development of Novel Synthetic Routes to the Epoxyketooctadecanoic Acids
    DEVELOPMENT OF NOVEL SYNTHETIC ROUTES TO THE EPOXYKETOOCTADECANOIC ACIDS (EKODES) AND THEIR BIOLOGICAL EVALUATION AS ACTIVATORS OF THE PPAR FAMILY OF NUCLEAR RECEPTORS By ROOZBEH ESKANDARI Submitted in partial fulfillment of the requirements for The Degree of Doctor of Philosophy Thesis Advisor: Gregory P. Tochtrop, Ph.D. Department of Chemistry CASE WESTERN RESERVE UNIVERSITY January, 2016 CASE WESTERN RESERVE UNIVERSITY SCHOOL OF GRADUATE STUDIES We hereby approve the thesis/dissertation of ROOZBEH ESKANDARI Candidate for the Ph.D degree *. (signed) Anthony J. Pearson, PhD (Chair of the committee) Gregory P. Tochtrop, PhD (Advisor) Michael G. Zagorski, PhD Blanton S. Tolbert, PhD Witold K. Surewicz, PhD (Department of Physiology and Biophysics) (date) 14th July, 2015 *We also certify that written approval has been obtained for any proprietary material contained therein. I dedicate this work to my sister Table of Contents Table of Contents ........................................................................................................................ i List of Tables .............................................................................................................................. vi List of Figures ........................................................................................................................... vii List of Schemes .......................................................................................................................... ix Acknowledgements ..................................................................................................................
    [Show full text]