A Review of Human Exposure to Microplastics and Insights Into Microplastics As Obesogens
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The Obesogen Hypothesis: Current Status and Implications for Human Health
Curr Envir Health Rpt (2014) 1:333–340 DOI 10.1007/s40572-014-0026-8 MECHANISMS OF TOXICITY (CJ MATTINGLY, SECTION EDITOR) The Obesogen Hypothesis: Current Status and Implications for Human Health Jerrold J. Heindel & Thaddeus T. Schug Published online: 20 September 2014 # Springer International Publishing AG (outside the USA) 2014 Abstract Obesity and diabetes have overtaken smoking as agreed upon that this obesity epidemic is the product of poor the number 1 preventable health determinate in the United nutrition and lack of exercise. However, obesity is a complex States. In its basic form, obesity is due to disruptions of the endocrine disease caused by disruption of many control sys- endocrine systems that control food intake, satiety, and meta- tems involving interaction between genetic and environmental bolic rate. Recent studies have identified a subclass of endo- cues such as nutrition, exercise, drugs, behavior, alterations in crine disrupting chemicals that interfere with hormonally reg- the microbiome, and exposure to environmental chemicals. ulated metabolic processes, especially during early develop- Genome wide association studies using large populations ment. These chemicals, called “obesogens,” may predispose have uncovered some 40 novel single nucleotide polymor- individuals to gain weight despite efforts to limit caloric intake phisms that are associated with increased body mass index and increase physical activity. Evidence suggests that chemi- (BMI), but together these genetic identifiers account for less cal exposures early in life can predispose individuals to weight than 5 % of the incidence of obesity [2]. Indeed, there are no gain through programming changes, which may enhance dys- known genetic mechanisms that can explain the remarkable functional eating behaviors later in life. -
Phthalate Testing ‐ Frequently Asked Questions Updated February, 2009
Phthalate Testing ‐ Frequently Asked Questions Updated February, 2009 Q. Which specific phthalates is the Consumer Products Safety Information Act (CPSIA) concerned about? A. The six phthalate plasticizers of interest are: Diisononyl phthalate (DINP), Di‐2‐ ethylhexylphthalate (DEHP, sometimes called DOP), di‐n‐octyl phthalate (DnOP), Di‐isodecyl phthalate (DIDP), butylbenzyl phthalate (BBP), and dibutyl phthalate (DBP). Q. What can Polymer Diagnostics Inc. (PDI) test? A. PDI can test raw materials, compounds and finished goods. Q. How does PDI perform the testing? A. Samples are initially extracted (or diluted), and then analyzed by Gas Chromatography‐Mass Spectrometry [GC‐MS]. Depending on the results, additional analyses may be done to verify results and insure accuracy. This helps reduce the potential for false positives. Q. What about false positives? A. Although GC‐MS can reduce the likelihood of mis‐identification, the complexity of many formulations cannot rule this out. Further refinements of the analysis conditions or use of other separation techniques helps to enhance the reliability of the results. In those cases where the interference cannot be eliminated, results will clearly state this fact. Q. What is the current standard for testing for phthalates? A. Some literature has cited ASTM 3421‐75 as applicable for this testing. This method has been discontinued by ASTM, and has not been replaced. The regulatory body responsible for the CPSIA is currently working on recommending an improved method, but this is still in the planning stage. Q. What are the current issues, if any, with the test methods? A. Any method recommended should use current analytical methodologies. -
162 Part 175—Indirect Food Addi
§ 174.6 21 CFR Ch. I (4–1–19 Edition) (c) The existence in this subchapter B Subpart B—Substances for Use Only as of a regulation prescribing safe condi- Components of Adhesives tions for the use of a substance as an Sec. article or component of articles that 175.105 Adhesives. contact food shall not be construed as 175.125 Pressure-sensitive adhesives. implying that such substance may be safely used as a direct additive in food. Subpart C—Substances for Use as (d) Substances that under conditions Components of Coatings of good manufacturing practice may be 175.210 Acrylate ester copolymer coating. safely used as components of articles 175.230 Hot-melt strippable food coatings. that contact food include the fol- 175.250 Paraffin (synthetic). lowing, subject to any prescribed limi- 175.260 Partial phosphoric acid esters of pol- yester resins. tations: 175.270 Poly(vinyl fluoride) resins. (1) Substances generally recognized 175.300 Resinous and polymeric coatings. as safe in or on food. 175.320 Resinous and polymeric coatings for (2) Substances generally recognized polyolefin films. as safe for their intended use in food 175.350 Vinyl acetate/crotonic acid copoly- mer. packaging. 175.360 Vinylidene chloride copolymer coat- (3) Substances used in accordance ings for nylon film. with a prior sanction or approval. 175.365 Vinylidene chloride copolymer coat- (4) Substances permitted for use by ings for polycarbonate film. 175.380 Xylene-formaldehyde resins con- regulations in this part and parts 175, densed with 4,4′-isopropylidenediphenol- 176, 177, 178 and § 179.45 of this chapter. -
Diisononyl Phthalate (DINP) C26H42O4
CAS 28553-12-0 Diisononyl Phthalate (DINP) C26H42O4 Summary of Health Effects In a study that looked at the effects on male Diisononyl phthalate (DINP) can lead to growth rats of perinatal exposure to several phthalates, of tumors in the liver, spleen and kidneys of DINP was one of three phthalates that altered animals and can affect how unborn babies sexual differentiation.4 Several animal studies develop. It may also cause cancer in humans. have demonstrated that DINP exposure increased the incidence of liver, spleen and 1 How is DINP used? kidney tumors. DINP is primarily used as a plasticizer or softener in polyvinyl chloride (PVC) products, DINP induces antiandrogenic affects in animals, and therefore can contribute to the cumulative including vinyl flooring, wire and cable risk from exposure to other antiandrogenic insulation, coated fabrics, gloves, toys, garden phthalates.5 hoses, artificial leather and footwear.1 DINP is also used in other products such as rubber, inks, pigments and paints.1 Exposure: How can a person come in contact with it? Toxicity: What are its health effects? A person can come in contact with DINP by The National Toxicology Program determined breathing in contaminated air, swallowing dust, through animal testing that DINP is a eating contaminated food, or from skin contact 6 developmental toxicant based on fetuses with consumer products. growing additional ribs at the high dose tested.2 The National Health and Nutrition Examination DINP is listed as a carcinogen on California’s Survey (NHANES) 2005-2006 results showed Proposition 65 list.3 that mono-(carboxyoctyl) phthalate, a metabolite (breakdown product) of DINP, is present in urine samples of 95.2% of the sampled U.S. -
Migration of Chemical Additives from Plastic Products a Literature Review
s REPORT M-1906 | 2020 Migration of chemical additives from plastic products A literature review COLOPHON Executive institution Norwegian Environment Agency Project manager for the contractor Contact person in the Norwegian Environment Agency Heidi Morka Marianne van der Hagen M-no Year Pages Contract number 1906 2020 18 [Contract number] Publisher The project is funded by Norwegian Environment Agency Norwegian Environment Agency Author(s) Clare Andvik Title – Norwegian and English Migrasjon av tilsetningsstoffer fra plastprodukter: En vitenskapelig gjennomgang av litteratur Migration of chemical additives from plastic products: A literature review Summary – sammendrag Plastic polymers are often incorporated with various “additives”, which have the potential to migrate from plastic products and cause harm to both humans and the environment. This literature review gives an overview of the migration of chemical additives from plastic products used in building/construction materials, electronics, and furnishings/upholstery. Our scope was products used in the home, to reflect the possible exposure to consumers within the product lifetime. We found that within building/construction materials, the release of phthalates from plastic flooring is commonly measured, with DEHP having the highest migration rate and migration rates increasing with temperature. Within electronics, brominated flame retardants are often measured, but it is challenging to compare studies when differing measurement units are utilised. TCPP was commonly measured as emitted -
Hazardous Substances in Plastic Materials
TA Hazardous substances in plastic 3017 materials 2013 Prepared by COWI in cooperation with Danish Technological Institute Preface This report is developed within the project of mapping of prioritized hazardous substances in plastic materials. The report presents key information on the most used plastic types and their characteristics and uses, as well as on hazardous substances used in plastics and present on the Norwegian Priority List of hazardous substances (“Prioritetslisten”) and/or the Candidate List under REACH, by August 2012. The aim of the report is to be a brief handbook on plastic types and hazardous substances in plastics providing knowledge on the characteristics and use of different plastic materials and the function, uses, concentration, release patterns, and alternatives of the hazardous substances, allowing the user to use the report as an introduction and overview on the most important hazardous substances in plastics and the plastic types, they primarily are used in. The development of the report has been supervised by a steering committee consisting of: Inger-Grethe England, Klima- og Forurensningsdirektoratet (chairman) Pia Linda Sørensen, Klima- og Forurensningsdirektoratet Erik Hansen, COWI, Denmark Nils H. Nilsson, Danish Technological Institute The report has been prepared by Erik Hansen, COWI-Denmark, Nils H. Nilsson, Danish Technological Institute, Delilah Lithner, COWI-Sweden and Carsten Lassen COWI- Denmark. Vejle, Denmark, 15. January 2013 Erik Hansen, COWI (project manager) 1 Content English Summary and -
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 -
Polyvinylchloride, Phthalates and Packaging
Page 29 | Bulletin 86 | July 2014 Polyvinylchloride, phthalates and packaging Plastics are synthetic resins, are either thermosetting or thermoplastic. Thermoplastic resins can be re-softened by heating, and include polyethylene (PE), polystyrene (PS), polypropylene (PP), and polyvinylchloride (PVC) which is very widely used in disposable medical devices. Polyvinylchloride (PVC) Di(2-ethylhexyl) phthalate (DEHP) Vinyl chloride (CH2=CHCl or chloroethylene) DEHP (sometimes referred to as bis is polymerized by free-radical initiators to (2-ethylhexyl) phthalate) is the diester of open the double bond and to link together phthalic acid and 2 ethylhexanol (Figure 2). vinyl chloride monomers, to form repeating Dr A M Walton units of polymers (Figure 1). Figure 2 The structure of di(2-ethylhexyl) phthalate DEHP. Anaesthesia ST 7, Figure 1 The phthalic moiety is common to all phthalates; University Hospital The chemical structure of vinyl chloride and PVC the pair of symmetrical aliphatic chains depends Southampton on the esterified alcohol PVC is a rigid structure at room temperature. Heating gives the molecules energy, widens the distance between between the molecules and softens the resin. To give PVC flexibility at room and body temperatures, plasticisers Dr J M T Pierce are added non-covalently to the PVC when Consultant Anaesthetist, At room temperature it is a colourless, oil- University Hospital molten and serve as molecular spacers so soluble viscous liquid and is used to form Southampton; RCoA when cooled the polymer has a softness even up to 40% of the mass of the PVC product. Environmental Advisor at room temperatures. The most commonly The annual global production of DEHP is used plasticisers are phthalates. -
Selected Plasticisers and Additional Sweeteners in the Nordic Environment Selected Plasticisers and Additional Sweeteners in the Nordic Environment
TemaNord 2013:505 TemaNord Ved Stranden 18 DK-1061 Copenhagen K www.norden.org Selected Plasticisers and Additional Sweeteners in the Nordic Environment Selected Plasticisers and Additional Sweeteners in the Nordic Environment The report Selected plasticisers and additional sweeteners in the Nordic Environment describes the findings of a Nordic environmental study. The study has been done as a screening, that is, it provides a snapshot of the occurrence of selected plasticisers and sweeteners, both in regions most likely to be polluted as well as in some very pristine environments. The pla- sticisers analysed were long chained phthalates and adipates, and the sweeteners analysed were aspartame, cyclamate and sucralose. The purpose of the screening was to elucidate levels and pathways of hitherto unrecognized pollutants. Thus the samples analysed were taken mainly from sewage lines, but also in recipients and biota, both in assumed hot-spot areas and in background areas. TemaNord 2013:505 ISBN 978-92-893-2464-9 ISBN 978-92-893-2464-9 9 789289 324649 TN2013505 omslag.indd 1 18-02-2013 10:25:36 Selected Plasticisers and Additional Sweeteners in the Nordic Environment Mikael Remberger, Lennart Kaj, Katarina Hansson, Hanna Andersson and Eva Brorström-Lundén, IVL Swedish Environmental Research Institute, Helene Lunder and Martin Schlabach, NILU, Norwegian Institute for Air Research TemaNord 2013:505 Selected Plasticisers and Additional Sweeteners in the Nordic Environment Mikael Remberger, Lennart Kaj, Katarina Hansson, Hanna Andersson and Eva Brorström-Lundén, IVL Swedish Environmental Research Institute, Helene Lunder and Martin Schlabach, NILU, Norwegian Institute for Air Research ISBN 978-92-893-2464-9 http://dx.doi.org/10.6027/TN2013-505 TemaNord 2013:505 © Nordic Council of Ministers 2013 Layout: Hanne Lebech/NMR Cover photo: Image Select Print: Rosendahls-Schultz Grafisk Copies: 150 Printed in Denmark This publication has been published with financial support by the Nordic Council of Ministers. -
Toxicity Review for Diisononyl Phthalate (DINP)
risk is performed to evaluate whether the chemical may be considered a “hazardous substance” under the FHSA. Purpose and Scope of the Report The primary purpose of the attached report is to complete the first two steps in the risk assessment process, that is, the hazard identification and dose response assessment. In addition, the report briefly summarizes published information relating to exposure, as well as published exposure and risk assessments. The sections on exposure and risk assessment are included to provide additional context for the reader, and as background for future risk assessments. However, quantitative exposure and risk assessments are beyond the scope of this report. Cumulative risks from exposure to multiple phthalates are also not included in this report, although they are briefly discussed. The information in this report will be provided to the Chronic Hazard Advisory Panel on Phthalates. This panel will convene in 2010 to assess the potential health effects of cumulative exposure to phthalates from all sources, including children’s articles and cosmetics. -2- Contents Summary ..............................................................................................................................v Abbreviations .................................................................................................................... vii 1. Introduction ...........................................................................................................1 2. Chemistry and Use ................................................................................................4 -
Chemicals and Obesity
CHEMICALS AND OBESITY While diet and exercise are important factors in the obesity epidemic, an emerging body of science demonstrates that exposures to chemical obesogens may be important contributors. A number of chemicals known to disrupt hormones also appear to affect the size and number of fat cells or hormones that regulate appetite and metabolism. The U.S. is confronting the growing rate of obesity as a major building materials. Hundreds of chemicals are recognized as public health problem. One-third of American children, and hormone disrupters that impact the delicate hormone balance two-thirds of adults, are obese or overweight.1 The direct costs in the human body. Hormone disrupters are especially harmful of treating obesity alone are $190 billion per year,2 which might because, like hormones themselves, they can exert health be as high as 16.5 percent of national health care spending.3 impacts even at minute levels of exposure and exposures in the While diet and exercise are widely recognized as important womb can have lifelong impacts. factors in the obesity epidemic, there is an emerging body of science showing that exposures to chemical obesogens may be important contributors. Obesogens are chemical agents Hormone disruption that promote fat accumulation and alter feeding behaviors A number of chemicals known to disrupt hormones also appear through various mechanisms, and we are all exposed to them to be obesogens.4,5 A 2011 National Institute of Environmental every day. Health Sciences (NIEHS) expert workshop concluded that the scientific literature supports a link between certain environ- mental chemicals and increased risk for obesity as well as Type 2 diabetes.6 Chemicals can affect the size and number of fat Widespread exposure cells or the hormones that regulate appetite and metabolism. -
Common Chemical Additives in Plastics
Journal of Hazardous Materials 344 (2018) 179–199 Contents lists available at ScienceDirect Journal of Hazardous Materials j ournal homepage: www.elsevier.com/locate/jhazmat Review An overview of chemical additives present in plastics: Migration, release, fate and environmental impact during their use, disposal and recycling a,∗ a,∗ b a a John N. Hahladakis , Costas A. Velis , Roland Weber , Eleni Iacovidou , Phil Purnell a School of Civil Engineering, University of Leeds, Woodhouse Lane, LS2 9JT, Leeds, United Kingdom b POPs Environmental Consulting, Lindenfirststr. 23, D.73527, Schwäbisch Gmünd, Germany h i g h l i g h t s g r a p h i c a l a b s t r a c t • Plastics are important in our society providing a range of benefits. • Waste plastics, nowadays, burden the marine and terrestrial environment. • Additives and PoTSs create complica- tions in all stages of plastics lifecycle. • Inappropriate use, disposal and recy- cling may lead to undesirable release of PoTSs. • Sound recycling of plastics is the best waste management and sustainable option. a r t i c l e i n f o a b s t r a c t Article history: Over the last 60 years plastics production has increased manifold, owing to their inexpensive, multipur- Received 22 July 2017 pose, durable and lightweight nature. These characteristics have raised the demand for plastic materials Received in revised form 2 October 2017 that will continue to grow over the coming years. However, with increased plastic materials production, Accepted 7 October 2017 comes increased plastic material wastage creating a number of challenges, as well as opportunities to Available online 9 October 2017 the waste management industry.