Comparative Metabolism and Distribution of 8-2 Fluorotelomer
Total Page:16
File Type:pdf, Size:1020Kb
Load more
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 -
DRAFT Indicators Biomonitoring: Perfluorochemicals (Pfcs)
America’s Children and the Environment, Third Edition DRAFT Indicators Biomonitoring: Perfluorochemicals (PFCs) EPA is preparing the third edition of America’s Children and the Environment (ACE3), following the previous editions published in December 2000 and February 2003. ACE is EPA’s compilation of children’s environmental health indicators and related information, drawing on the best national data sources available for characterizing important aspects of the relationship between environmental contaminants and children’s health. ACE includes four sections: Environments and Contaminants, Biomonitoring, Health, and Special Features. EPA has prepared draft indicator documents for ACE3 representing 23 children's environmental health topics and presenting a total of 42 proposed children's environmental health indicators. This document presents the draft text, indicator, and documentation for the PFCs topic in the Biomonitoring section. THIS INFORMATION IS DISTRIBUTED SOLELY FOR THE PURPOSE OF PRE- DISSEMINATION PEER REVIEW UNDER APPLICABLE INFORMATION QUALITY GUIDELINES. IT HAS NOT BEEN FORMALLY DISSEMINATED BY EPA. IT DOES NOT REPRESENT AND SHOULD NOT BE CONSTRUED TO REPRESENT ANY AGENCY DETERMINATION OR POLICY. For more information on America’s Children and the Environment, please visit www.epa.gov/ace. For instructions on how to submit comments on the draft ACE3 indicators, please visit www.epa.gov/ace/ace3drafts/. March 2011 DRAFT: DO NOT QUOTE OR CITE Biomonitoring: Perfluorochemicals 1 Perfluorochemicals (PFCs) 2 3 Perfluorochemicals (PFCs) are a group of manmade chemicals that have been used since the 4 1950s in many consumer products.1 The structure of these chemicals makes them very stable, 5 hydrophobic (water-repelling), and oleophobic (oil-repelling). -
And Polyfluoroalkyl Substances – Chemical Variation and Applicability of Current Fate Models
CSIRO PUBLISHING Environ. Chem. 2020, 17, 498–508 Research Paper https://doi.org/10.1071/EN19296 Investigating the OECD database of per- and polyfluoroalkyl substances – chemical variation and applicability of current fate models Ioana C. Chelcea,A Lutz Ahrens,B Stefan O¨ rn,C Daniel MucsD and Patrik L. Andersson A,E ADepartment of Chemistry, Umea˚ University, SE-901 87 Umea˚, Sweden. BDepartment of Aquatic Sciences and Assessment, Swedish University of Agricultural Sciences (SLU), Box 7050, SE-750 07 Uppsala, Sweden. CDepartment of Biomedical Sciences and Veterinary Public Health, Swedish University of Agricultural Sciences (SLU), SE-750 07 Uppsala, Sweden. DRISE SP – Chemical and Pharmaceutical Safety, Forskargatan 20, 151 36 So¨derta¨lje, Sweden. ECorresponding author. Email: [email protected] Environmental context. A diverse range of materials contain organofluorine chemicals, some of which are hazardous and widely distributed in the environment. We investigated an inventory of over 4700 organofluorine compounds, characterised their chemical diversity and selected representatives for future testing to fill knowledge gaps about their environmental fate and effects. Fate and property models were examined and concluded to be valid for only a fraction of studied organofluorines. Abstract. Many per- and polyfluoroalkyl substances (PFASs) have been identified in the environment, and some have been shown to be extremely persistent and even toxic, thus raising concerns about their effects on human health and the environment. Despite this, little is known about most PFASs. In this study, the comprehensive database of over 4700 PFAS entries recently compiled by the OECD was curated and the chemical variation was analysed in detail. -
Cross-Sectional Study of the Association Between Serum Perfluorinated Alkyl Acid Concentrations and Dental Caries Among US Adolescents (NHANES 1999–2012)
Open access Research BMJ Open: first published as 10.1136/bmjopen-2018-024189 on 5 February 2019. Downloaded from Cross-sectional study of the association between serum perfluorinated alkyl acid concentrations and dental caries among US adolescents (NHANES 1999–2012) Nithya Puttige Ramesh,1 Manish Arora,2 Joseph M Braun1 To cite: Puttige Ramesh N, ABSTRACT Strengths and limitations of this study Arora M, Braun JM. Cross- Study objectives Perfluoroalkyl acids (PFAAs) are a class sectional study of the of anthropogenic and persistent compounds that may ► Our study contributes to a gap in the literature by association between serum impact some biological pathways related to oral health. perfluorinated alkyl acid examining the relationship between perfluoroalkyl The objective of our study was to estimate the relationship concentrations and dental caries acid exposure and dental caries prevalence among between dental caries prevalence and exposure to four among US adolescents (NHANES adolescents, which, to the best of our knowledge, PFAA: perfluorooctanoic acid (PFOA), perfluorononanoic 1999–2012). BMJ Open has not been examined before. 2019;9:e024189. doi:10.1136/ acid (PFNA), perfluorohexane sulfonic acid (PFHxS) and ► The strengths of our study include the large sample perfluorooctane sulfonic acid (PFOS) in a nationally bmjopen-2018-024189 size (2869 participants) and the nationally repre- representative sample of US adolescents. Prepublication history and sentative nature of the National Health and Nutrition ► Setting/Design We analysed cross-sectional data from additional material for this Examination Survey (NHANES). the National Health and Nutrition Examination Survey from paper are available online. To ► Although we adjusted for potential confounders, 1999 to 2012 for 12–19-year-old US adolescents. -
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 ........................................................................................................ -
Us 2018 / 0296525 A1
UN US 20180296525A1 ( 19) United States (12 ) Patent Application Publication (10 ) Pub. No. : US 2018/ 0296525 A1 ROIZMAN et al. ( 43 ) Pub . Date: Oct. 18 , 2018 ( 54 ) TREATMENT OF AGE - RELATED MACULAR A61K 38 /1709 ( 2013 .01 ) ; A61K 38 / 1866 DEGENERATION AND OTHER EYE (2013 . 01 ) ; A61K 31/ 40 ( 2013 .01 ) DISEASES WITH ONE OR MORE THERAPEUTIC AGENTS (71 ) Applicant: MacRegen , Inc ., San Jose , CA (US ) (57 ) ABSTRACT ( 72 ) Inventors : Keith ROIZMAN , San Jose , CA (US ) ; The present disclosure provides therapeutic agents for the Martin RUDOLF , Luebeck (DE ) treatment of age - related macular degeneration ( AMD ) and other eye disorders. One or more therapeutic agents can be (21 ) Appl. No .: 15 /910 , 992 used to treat any stages ( including the early , intermediate ( 22 ) Filed : Mar. 2 , 2018 and advance stages ) of AMD , and any phenotypes of AMD , including geographic atrophy ( including non -central GA and Related U . S . Application Data central GA ) and neovascularization ( including types 1 , 2 and 3 NV ) . In certain embodiments , an anti - dyslipidemic agent ( 60 ) Provisional application No . 62/ 467 ,073 , filed on Mar . ( e . g . , an apolipoprotein mimetic and / or a statin ) is used 3 , 2017 . alone to treat or slow the progression of atrophic AMD Publication Classification ( including early AMD and intermediate AMD ) , and / or to (51 ) Int. CI. prevent or delay the onset of AMD , advanced AMD and /or A61K 31/ 366 ( 2006 . 01 ) neovascular AMD . In further embodiments , two or more A61P 27 /02 ( 2006 .01 ) therapeutic agents ( e . g ., any combinations of an anti - dys A61K 9 / 00 ( 2006 . 01 ) lipidemic agent, an antioxidant, an anti- inflammatory agent, A61K 31 / 40 ( 2006 .01 ) a complement inhibitor, a neuroprotector and an anti - angio A61K 45 / 06 ( 2006 .01 ) genic agent ) that target multiple underlying factors of AMD A61K 38 / 17 ( 2006 .01 ) ( e . -
PFOA) and Suggested As PFCA Precursor Compounds (7, 8)
within a few days. Fluorotelomer alcohols (FTOHs) have been Formation of C7F15COOH (PFOA) and suggested as PFCA precursor compounds (7, 8). FTOHs are linear fluorinated alcohols with the formula CnF2n+1CH2CH2- Other Perfluorocarboxylic Acids OH (n ) 2, 4, 6, ...). The telomerization process results in during the Atmospheric Oxidation of even-numbered linear chains, and the alcohols are named according to the number of fluorinated and hydrogenated 8:2 Fluorotelomer Alcohol carbons, e.g., C8F17CH2CH2OH is 8:2 fluorotelomer alcohol (8:2 FTOH). Global production of FTOHs is 12 106 kg year-1, × T . J . W A L L I N G T O N , * , † M . D . H U R L E Y , † and sales are approximately $700 million annually (9). J . X I A , ‡ D . J . W U E B B L E S , ‡ S . S I L L M A N , § Fluorotelomer alcohols are volatile, have been observed in A . I T O , § J . E . P E N N E R , § D . A . E L L I S , | the North American atmosphere in significant concentrations -3 J . M A R T I N , | S . A . M A B U R Y , | (17-135 pg m ) (10, 11), and have an atmospheric lifetime O . J . N I E L S E N , ⊥ A N D (10-20 days) sufficient for widespread hemispheric distribu- M . P . S U L B A E K A N D E R S E N ⊥ tion (7, 12). C8F17CH2CH2OH (8:2 FTOH) is the most important Ford Motor Company, SRL-3083, P.O. Box 2053, Dearborn, FTOH and is the subject of the present study. -
Biotransformation of AFFF Component 6:2 Fluorotelomer Thioether Amido
Biotransformation of AFFF Component 6:2 Fluorotelomer Thioether Amido Sulfonate Generates 6:2 Fluorotelomer Thioether Carboxylate under Sulfate-Reducing Conditions Shan Yi†, Katie C. Harding-Marjanovic‡, Erika F. Houtz§, Ying Gao∥, Jennifer E. Lawrence†, Rita V. Nichiporuk⊥, Anthony T. Iavarone⊥, Wei-Qin Zhuang#, Martin Hansen@, Jennifer A. Field∇, David L. Sedlak†, and Lisa Alvarez- Cohen*†● † Department of Civil and Environmental Engineering, University of California, Berkeley, California 94720, United States ‡ Exponent, Pasadena, California 91106, United States § Arcadis, San Francisco, California 94104, United States ∥ Institute of Desertification Studies, Chinese Academy of Forestry, Beijing 100091, China ⊥ The California Institute for Quantitative Biosciences (QB3), University of California, Berkeley, California 94720, United States # Department of Civil and Environmental Engineering, University of Auckland, Auckland 1142, New Zealand @ Department of Environmental Science, Aarhus University, 4000 Roskilde, Denmark ∇ Department of Molecular and Environmental Toxicology, Oregon State University, Corvallis, Oregon 97331, United States ● Earth and Environmental Sciences Division, Lawrence Berkeley National Laboratory, Cyclotron Road, Berkeley, California 94720, United States *Department of Civil and Environmental Engineering, 726 Davis Hall, University of California, Berkeley, CA 94720-1710. Phone: (510) 643-5969. Fax: (510) 642-7483. E-mail: [email protected]. Abstract The fate of per- and polyfluoroalkyl substances (PFASs) in aqueous film- forming foams (AFFFs) under anaerobic conditions has not been well characterized, leaving major gaps in our understanding of PFAS fate and transformation at contaminated sites. In this study, the biotransformation of 6:2 fluorotelomer thioether amido sulfonate (6:2 FtTAoS), a component of several AFFF formulations, was investigated under sulfate-reducing conditions in microcosms inoculated with either pristine or AFFF-impacted solids. -
In Vitro and in Vivo Estrogenic Effects of Fluorotelomer Alcohols in Medaka (Oryzias Latipes)
Interdisciplinary Studies on Environmental Chemistry—Biological Responses to Chemical Pollutants, Eds., Y. Murakami, K. Nakayama, S.-I. Kitamura, H. Iwata and S. Tanabe, pp. 291–301. © by TERRAPUB, 2008. In vitro and in vivo Estrogenic Effects of Fluorotelomer Alcohols in Medaka (Oryzias latipes) Hiroshi ISHIBASHI1, Ryoko YAMAUCHI1, Munekazu MATSUOKA1, Joon-Woo KIM1, Masashi HIRANO1, Akemi YAMAGUCHI2, Nobuaki TOMINAGA2 and Koji ARIZONO1 1Faculty of Environmental and Symbiotic Sciences, Prefectural University of Kumamoto, 3-1-100 Tsukide, Kumamoto 862-8502, Japan 2Department of Chemical and Biological Engineering, Ariake National College of Technology, 150 Higashihagio-machi, Omuta, Fukuoka 836-8585, Japan (Received 15 May 2008; accepted 31 July 2008) Abstract—The present study demonstrates the estrogenic effects of two fluorotelomer alcohols, such as 1H,1H,2H,2H-perfluorooctan-1-ol (6:2 FTOH) and 1H,1H,2H,2H-perfluorodecan-1-ol (8:2 FTOH), in medaka (Oryzias latipes). An in vitro yeast two-hybrid assay indicated a significant, dose- dependent interaction between medaka estrogen receptor α (ERα) and coactivator TIF2 upon treatment with 6:2 FTOH or 8:2 FTOH. In contrast, no interaction with the ERα was observed upon treatment with perfluorooctane sulfonate (PFOS), perfluorooctanoic acid (PFOA), perfluorononanoic acid (PFNA), perfluorododecanoic acid (PFDA) or perfluoroundecanoic acid (PFUnDA). Expression analysis of hepatic vitellogenin (VTG) protein showed estrogenic potentials with, 6:2 FTOH and 8:2 FTOH, indicative of the induction of VTG synthesis in the livers of male medaka. We also investigated mRNA expression levels of two ER subtypes and two VTGs in the livers of male medaka following exposure to FTOHs. Quantitative real-time PCR analyses revealed that hepatic ERα, VTG I, and VTG II mRNA responded rapidly to FTOHs such as 6:2 FTOH and 8:2 FTOH after 8-h exposure, whereas no effects of these compounds on ERβ mRNA transcription were observed. -
Semi-Volatile Fluorinated Organic Compounds in Asian and Pacific Northwestern US Air Masses
2 AN ABSTRACT OF THE THESIS OF Arkadiusz M. Piekarz for the degree of Master of Science in Chemistry presented on March 28, 2007. Title: Semi-volatile Fluorinated Organic Compounds in Asian and Pacific Northwestern U.S. Air Masses. Abstract approved: Staci Simonich Current studies suggest that perfluorinated organic compounds, such as fluorotelomer alcohols (FtOHs) in the troposphere, may be precursors of perfluorocarboxylic acids and perfluorosulfonates in remote regions. Fluorinated organic compounds were investigated in archived extracts collected from remote locations in Okinawa, Japan (HSO) and Mount Bachelor, Oregon (MBO) during the springs of 2004 (MBO and HSO) and 2006 (MBO only). These high volume air samples were subjected to pressurized liquid extraction, concentrated, and analyzed by GC/MS. FtOHs were measured in both HSO and MBO air masses, though MBO had significantly higher concentrations. We identified fluorotelomer olefins (in HSO air) and 8:2 fluorotelomer acrylate (in MBO 2006 air) for the first time in published literature. N-Ethyl 3 perfluorooctane sulfonamide (N-EtFOSA), N-Methyl perfluorooctane sulfonamido ethanol (N-MeFOSE), and N-Ethyl perfluorooctane sulfonamido ethanol (N-EtFOSE) were measured in HSO and MBO air masses, but detected less frequently than FtOHs. 6:2 fluorotelomer acrylate, perfluorooctane sulfonamido acrylates, perfluorobutane sulfonamide, and perfluorobutane sulfonamido ethanol were not detected in any air samples from this study. For MBO 2006, the sources of fluorotelomer alcohols were investigated using HYSPLIT back trajectories, residual fluorinated product signatures, and correlations with semi-volatile organic compounds (SOCs). FtOH concentrations during MBO 2006 were not significantly correlated (p-value > 0.05) with the amount of time an air trajectory spent in a specific source region such as California, Washington, Oregon, and Canada. -
Potential PFOA Precursors
Potential PFOA Precursors Literature study and theoretical assessment of abiotic degradation pathways leading to PFOA. M-231/2014 Claus Jørgen Nielsen CTCC, Department of Chemistry University of Oslo This page is intentionally left blank Potential PFOA Precursors Literature study and theoretical assessment of abiotic degradation pathways leading to PFOA. Claus Jørgen Nielsen CTCC, Department of Chemistry, University of Oslo This page is intentionally left blank 1 Preface The Norwegian Environment Agency, in cooperation with German Environment Authorities, is preparing a report proposing regulations on PFOA (perfluorooctanoic acid), its salts and precursors. PFOA (or its ammonium salt), is mainly used as a processing aid in the production of fluoropolymers; i.e. polytetrafluoroethylene (PTFE) and polyvinylidenefluoride (PVDF). Other PFOA sources are fluorotelomers, which are not produced using PFOA, but which may contain low levels of PFOA. There are a number of products containing PFOA such as carpet care solutions, sealants, floor waxes, paints, impregnating agents, fire fighting foam, ski wax and surface coatings of carpets, textiles, paper and leather. PFOA is found in the environment and in people all over the world. PFOA is degraded very slowly in nature and is long-range transported to the Arctic. PFOA is listed as a priority pollutant covered by the national goal that emissions should be eliminated by 2020. The overall objective of the present project is to summarize relevant information available in the open literature to provide an overall assessment of relevant precursors including possible grouping, and to evaluate possible routes to provide documentation, where missing, on the potential of abiotic degradation resulting in PFOA The present report summarises a classification of potential PFOA precursors and outlines the transformation routes leading to PFOA. -
Perfluoroalkylated Acids and Related Compounds (PFAS) in the Swedish Environment
Perfluoroalkylated acids and related compounds (PFAS) in the Swedish environment Chemistry Sources Exposure Ulf Järnberg Katrin Holmström Department of Applied Environmental Science, ITM Stockholm University Bert van Bavel Anna Kärrman Man Technology and Science, MTM Örebro University I Preface This report summarizes the results of several investigations conducted in Sweden during the years 2002-2005 concerning perfluoroalkylated substances (PFAS). The projects were mainly funded by the Swedish Environmental Protection Agency (S- EPA) within the environmental monitoring programs but for this compilation results from other investigations have also been included to provide a more complete overview of the present situation regarding the use of and pollution status for PFAS in Sweden. These investigations were funded by the Swedish Rescue Services Agency, the Regional County of Västra Götaland, Svenskt Vatten (VA-forsk grant nr.23:101 ) and the Nordic Council. This report also contains a compilation of literature data and information gathered from representatives of Swedish companies, authorities, and organisations. Patent information has been included and referenced in order to provide a more general picture of highly fluorinated organic compounds. It should be stressed however, that patent descriptions relate to the potential use and do not necessarily reflect the actual use. A list of information sources is given at the end of the report. The beginning of the report provides an outline of fluorinated organic compounds in general and is intended to provide a basis for the following detailed descriptions of the perfluoroalkyl substances (PFAS) that where selected by the S-EPA and Swedish Chemicals Inspectorate (KemI) for initial screening in the Swedish urban environment.