Perfluorooctane Sulfonate (PFOS) and Perfluorooctanoic Acid (PFOA) November 2017 TECHNICAL FACT SHEET – PFOS and PFOA
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Activated Carbon in Sediment Remediation
ACTIVATED CARBON IN SEDIMENT REMEDIATION. BENEFITS, RISKS AND PERSPECTIVES Darya KUPRYIANCHYK Thesis committee Promoter Prof. dr. A.A. Koelmans Professor Water and Sediment Quality Co-promoter Dr. ir. J.T.C. Grotenhuis Assistant professor Environmental Technology Other members Prof. dr. R.N.J. Comans, Wageningen University Prof. dr. ir. W.J.G.M. Peijnenburg, RIVM, Leiden University Prof. dr. ir. A.J. Hendriks, Radboud University Nijmegen Dr. ir. M.T.O. Jonker, Utrecht University This research was conducted under the auspices of the Graduate School for Socio-Economic and Natural Sciences of the Environment (SENSE). ACTIVATED CARBON IN SEDIMENT REMEDIATION. BENEFITS, RISKS AND PERSPECTIVES Darya KUPRYIANCHYK Thesis submitted in fulfilment of the requirements for the degree of doctor at Wageningen University by the authority of the Rector Magnificus Prof. dr. M.J. Kropff, in the presence of the Thesis Committee appointed by the Academic Board to be defended in public on Friday 1 February 2013 at 4.00 p.m. in the Aula Darya Kupryianchyk Activated carbon in sediment remediation. Benefits, risks and perspectives 264 pages. Thesis, Wageningen University, Wageningen, The Netherlands (2013) With references and summaries in English and Dutch ISBN 978-94-6173-431-0 To my mother “who told me songs were for the birds, then taught me all the tunes I know and a good deal of the words.” Ken Kesey Contents Chapter 1. General introduction....................................................................................... 9 Chapter 2. In situ remediation of contaminated sediments using carbonaceous materials. A review......................................................................................... 17 Chapter 3. In situ sorption of hydrophobic organic compounds to sediment amended with activated carbon..................................................................................... -
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 -
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 ............................................................................................................... -
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 ........................................................................................................ -
Fish Bioconcentration Data Requirement: Guidance for Selection of Number of Treatment Concentrations
Document ID No.: EPA 705-G-2020-3708 Fish Bioconcentration Data Requirement: Guidance for Selection of Number of Treatment Concentrations [Supplement to OCSPP Test Guideline 850.1730] July 15, 2020 Disclaimer: The contents of this document do not have the force and effect of law and are not meant to bind the public in any way. This document is intended only to provide clarity to the public regarding existing requirements under the law or agency policies. Office of Pesticide Programs Office of Chemical Safety and Pollution Prevention U.S. Environmental Protection Agency I. Purpose The purpose of this document is to clarify EPA recommendations for the number of treatment concentrations needed to result in acceptable fish bioconcentration factor (BCF) studies for pesticide registration. EPA routinely requires BCF studies to determine whether pesticide active ingredients have the potential to accumulate in fish, enter the food chain, and cause adverse effects in fish-eating predators such as aquatic mammals and birds of prey. In April 2017, EPA was approached by an outside party, the National Centre for the Replacement, Refinement and Reduction of Animals in Research (NC3R), with a suggestion to modify the test guideline for the BCF study to reduce the number of animals used in BCF testing, by reducing the number of concentration levels used from three (two positive doses and one control) to two (one positive level and one control). NC3R stated that this would be “[i]n the interest of international harmonization and reducing unnecessary animal testing” because “[a]t the moment the Japanese and US EPA guideline require that two concentrations are always tested, which is in contrast to the OECD Test Guideline[1]; therefore, many companies are understandably continuing to test two concentrations to ensure acceptance within these regions.” This modification has the potential to reduce the number of fish used by one-third. -
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. -
Toxicity and Assessment of Chemical Mixtures
Toxicity and Assessment of Chemical Mixtures Scientific Committee on Health and Environmental Risks SCHER Scientific Committee on Emerging and Newly Identified Health Risks SCENIHR Scientific Committee on Consumer Safety SCCS Toxicity and Assessment of Chemical Mixtures The SCHER approved this opinion at its 15th plenary of 22 November 2011 The SCENIHR approved this opinion at its 16th plenary of 30 November 2011 The SCCS approved this opinion at its 14th plenary of 14 December 2011 1 Toxicity and Assessment of Chemical Mixtures About the Scientific Committees Three independent non-food Scientific Committees provide the Commission with the scientific advice it needs when preparing policy and proposals relating to consumer safety, public health and the environment. The Committees also draw the Commission's attention to the new or emerging problems which may pose an actual or potential threat. They are: the Scientific Committee on Consumer Safety (SCCS), the Scientific Committee on Health and Environmental Risks (SCHER) and the Scientific Committee on Emerging and Newly Identified Health Risks (SCENIHR) and are made up of external experts. In addition, the Commission relies upon the work of the European Food Safety Authority (EFSA), the European Medicines Agency (EMA), the European Centre for Disease prevention and Control (ECDC) and the European Chemicals Agency (ECHA). SCCS The Committee shall provide opinions on questions concerning all types of health and safety risks (notably chemical, biological, mechanical and other physical risks) of non- food consumer products (for example: cosmetic products and their ingredients, toys, textiles, clothing, personal care and household products such as detergents, etc.) and services (for example: tattooing, artificial sun tanning, etc.). -
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 -
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. -
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. -
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 -
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.