General Comments Component(S) in Which (%) Substances Is Contained 1 Antimony 1309-64-4 Carc Cat
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Date of Issue: 17 June 2015 SAFETY DATA SHEET 1. SUBSTANCE AND SOURCE IDENTIFICATION Product Identifier SRM Number: 1877 SRM Name: Beryllium Oxide Powder Other Means of Identification: Not applicable. Recommended Use of This Material and Restrictions of Use This Standard Reference Material (SRM) is intended for use in laboratory analysis and health research for the development and validation of analytical methods and instruments used to determine beryllium, as well as for proficiency testing of laboratories involved in beryllium determinations. A unit of SRM 1877 consists of one bottle containing 20 g of beryllium oxide powder. Company Information National Institute of Standards and Technology Standard Reference Materials Program 100 Bureau Drive, Stop 2300 Gaithersburg, Maryland 20899-2300 Telephone: 301-975-2200 Emergency Telephone ChemTrec: FAX: 301-948-3730 1-800-424-9300 (North America) E-mail: [email protected] +1-703-527-3887 (International) Website: http://www.nist.gov/srm 2. HAZARDS IDENTIFICATION Classification Physical Hazard: Not classified. Health Hazard: Acute Toxicity, Inhalation Category 2 Skin Corrosion/Irritation Category 2 Serious Eye Damage/Irritation Category 2B Skin Sensitization Category 1 Carcinogenicity Category 1A STOT-Repeat Exposure Category 1 Label Elements Symbol Signal Word DANGER Hazard Statement(s) H330 Fatal if inhaled. H315+H320 Causes skin and eye irritation. H317 May cause an allergic skin reaction. H350 May cause lung cancer. H372 Causes damage to lungs through prolonged or repeated inhalation. Precautionary Statement(s) P201 Obtain special instructions before use. P202 Do not handle until all safety precautions have been read and understood. P260 Do not breathe dust. P264 Wash hands thoroughly after handling. -
Exposure Data
BERYLLIUM AND BERYLLIUM eOMPOUNDS Beryllium and beryllium compounds were considered by previous Working Groups, In 1971,1979 and 1987 (lARe, 1972, 1980, 1987a). New data have since become available, and these are included in the present monograph and have been taken into consideration In the evaluation. The agents considered herein Include (a) metallic beryllium, (b) beryllium- aluminium and -copper alloys and (c) some beryllum compounds. 1. Exposure Data 1.1 Chemical and physical data and analysis 1.1.1 Synonyms, trade names and molecular formulae Synonyms, trade names and molecular formulae for beryllium, beryllum-aluminium and -copper alloys and certain beryllium compounds are presented in Thble 1. The list is not exhaustive, nor does it comprise necessarily the most commercially important beryllum- containing substances; rather, it indicates the range of beryllum compounds available. 1. 1.2 Chemical and physical properties of the pure substances Selected chemical and physical properties of beryllium, beryllum-aluminium and -copper alloys and the beryllium compounds covered in this monograph are presented in Thble 2. The French chemist Vauquelin discovered beryllium in 1798 as the oxide, while analysing emerald to prove an analogous composition (Newland, 1984). The metallc element was first isolated in independent experiments by Wöhler (1828) and Bussy (1828), who called it 'glucinium' owing to the sweet taste of its salts; that name is stil used in the French chemical literature. Wöhler's name 'beryllum' was offcially recognized by IUPAe in 1957 (WHO, 1990). The atomic weight and corn mon valence of beryllum were originally the subject of much controversy but were correctly predicted by Mendeleev to be 9 and + 2, respectively (Everest, 1973). -
Generation of Carbon Dioxide and Mobilization of Antimony Trioxide by Fungal Decomposition of Building Materials John D
University of South Florida Scholar Commons Graduate Theses and Dissertations Graduate School 3-25-2005 Generation of Carbon Dioxide and Mobilization of Antimony Trioxide by Fungal Decomposition of Building Materials John D. Krause University of South Florida Follow this and additional works at: https://scholarcommons.usf.edu/etd Part of the American Studies Commons Scholar Commons Citation Krause, John D., "Generation of Carbon Dioxide and Mobilization of Antimony Trioxide by Fungal Decomposition of Building Materials" (2005). Graduate Theses and Dissertations. https://scholarcommons.usf.edu/etd/730 This Dissertation is brought to you for free and open access by the Graduate School at Scholar Commons. It has been accepted for inclusion in Graduate Theses and Dissertations by an authorized administrator of Scholar Commons. For more information, please contact [email protected]. Generation of Carbon Dioxide and Mobilization of Antimony Trioxide by Fungal Decomposition of Building Materials by John D. Krause A dissertation submitted in partial fulfillment of the requirements for the degree of Doctor of Philosophy Department of Environmental and Occupational Health College of Public Health University of South Florida Major Professor: Yehia Y. Hammad, Sc.D. Noreen D. Poor, Ph.D. Ann C. Debaldo, Ph.D. Diane Te Strake, Ph.D. Date of Approval: March 25, 2005 Keywords: mold, mould, carbon dioxide, antimony trioxide, flame retardant © Copyright 2005, John D. Krause Dedication For their love, support, patience and understanding throughout this endeavor, I dedicate this work to my family, daughter, and most of all, my loving wife. Acknowledgements I would like to acknowledge the following individuals and companies for their assistance in this research. -
Toxicological Profile for Beryllium
BERYLLIUM 19 3. HEALTH EFFECTS 3.1 INTRODUCTION The primary purpose of this chapter is to provide public health officials, physicians, toxicologists, and other interested individuals and groups with an overall perspective on the toxicology of beryllium. It contains descriptions and evaluations of toxicological studies and epidemiological investigations and provides conclusions, where possible, on the relevance of toxicity and toxicokinetic data to public health. A glossary and list of acronyms, abbreviations, and symbols can be found at the end of this profile. 3.2 DISCUSSION OF HEALTH EFFECTS BY ROUTE OF EXPOSURE To help public health professionals and others address the needs of persons living or working near hazardous waste sites, the information in this section is organized first by route of exposure (inhalation, oral, and dermal) and then by health effect (death, systemic, immunological, neurological, reproductive, developmental, genotoxic, and carcinogenic effects). These data are discussed in terms of three exposure periods: acute (14 days or less), intermediate (15–364 days), and chronic (365 days or more). Levels of significant exposure for each route and duration are presented in tables and illustrated in figures. The points in the figures showing no-observed-adverse-effect levels (NOAELs) or lowest-observed-adverse-effect levels (LOAELs) reflect the actual doses (levels of exposure) used in the studies. LOAELS have been classified into "less serious" or "serious" effects. "Serious" effects are those that evoke failure in a biological system and can lead to morbidity or mortality (e.g., acute respiratory distress or death). "Less serious" effects are those that are not expected to cause significant dysfunction or death, or those whose significance to the organism is not entirely clear. -
4. Inorganic Flame Retardants. Plastics Can Be Given Flame Retardant Characteristics by Introducing Elements of Organic, Inorganic and Halogen Origin
4. Inorganic Flame Retardants. Plastics can be given flame retardant characteristics by introducing elements of organic, inorganic and halogen origin. Such elements include magnesium, aluminium, phosphorous, molybdenum, antimony, tin, chlorine and bromine. Flame retardants are added in either the manufacturing step of the polymer or the compounding step of the polymeric article. Phosphorous bromine and chlorine are usually included as some organic compound. Inorganic flame retardants are usually added together with other flame retardants to provide a more efficient flame retardant action through synergism. Halogen flame retardants usually need an addition of about 40% in order to be effective, and this affects the properties of the polymer quite negatively. Structural integrity of the polymer article is often very important, and a drastic decrease in strength and other mechanical properties is simply not acceptable. The efficiency of halogen flame retardants is often enhanced by the addition of inorganic flame retardants. A smaller mass percentage halogen flame retardant is now needed, so the adverse effect on the polymer properties is also reduced (Touval, 1993) . 4.1 Antimony Compounds The antimony compounds used for flame retardancy include antimony trioxide, antimony pentoxide and antimony-metal compounds. In 1990 in the United States alone, the use of antimony trioxide amounted to 20 000 metric tons just for the flame retardancy of plastics. Antimony oxide is readily found in nature but in very impure form. This is not suitable for 29 direct use as flame retardant, so antimony oxide is often rather produced from antimony metal. There are therefore many different grades of antimony oxide that can be used for flame retardants. -
"Beryllium Oxide Digestion Optimization at the Savannah River Site"
"Beryllium Oxide Digestion Optimization at the Savannah River Site" by Davin Jagnandan November, 2002 ==' ¥---- ; A paper submitted to the faculty of the University of North Carolina at Chapel Hill in partial fulfillment of the requirements for the degree of Master of Public Health in the School of Public Health Abstract Chronic beryllium disease (CBD) is a debilitating lung disorder affecting an estimated 4.6% of past nuclear weapons and beryllium manufacturing workers. The Chronic Beryllium Disease Prevention Program, as set up by the U.S. Department of Energy (DOE), establishes guidelines for maintaining acceptable exposure levels in all beryllium manufacturing facilities. These exposure levels are based on the measuring of total beryllium which includes beryllium metal, beryllium salts, beryllium alloys and beryllium oxide. The most sensitive detection instruments used in industrial hygiene sampling measure beryllium in a solubilized form . Beryllium oxide, in particular, has been shown to resist solubilization unless it is performed in the presence of strong acid(s). This poses a problem for industrial hygienists because beryllium oxide has been shown to have a high level oftoxicity due to its small size and moderate solubility. The current Ip digestion method (EPA 3050B) for all metals at the Savannah River Site 1 involves the use of nitric and hydrochloric acids. It was hypothesized that 1 this method was inadequate for the complete digestion of beryllium oxide. This study examines this issue by comparing method 3050B with two other acid digestion methods. Once the most effective of the three methods was determined, optimization factors such as settling time, heating/reflux time, and hydrogen peroxide addition were examined. -
123. Antimony
1998:11 The Nordic Expert Group for Criteria Documentation of Health Risks from Chemicals 123. Antimony John Erik Berg Knut Skyberg Nordic Council of Ministers arbete och hälsa vetenskaplig skriftserie ISBN 91–7045–471–x ISSN 0346–7821 http://www.niwl.se/ah/ah.htm National Institute for Working Life National Institute for Working Life The National Institute for Working Life is Sweden's center for research and development on labour market, working life and work environment. Diffusion of infor- mation, training and teaching, local development and international collaboration are other important issues for the Institute. The R&D competence will be found in the following areas: Labour market and labour legislation, work organization and production technology, psychosocial working conditions, occupational medicine, allergy, effects on the nervous system, ergonomics, work environment technology and musculoskeletal disorders, chemical hazards and toxicology. A total of about 470 people work at the Institute, around 370 with research and development. The Institute’s staff includes 32 professors and in total 122 persons with a postdoctoral degree. The National Institute for Working Life has a large international collaboration in R&D, including a number of projects within the EC Framework Programme for Research and Technology Development. ARBETE OCH HÄLSA Redaktör: Anders Kjellberg Redaktionskommitté: Anders Colmsjö och Ewa Wigaeus Hjelm © Arbetslivsinstitutet & författarna 1998 Arbetslivsinstitutet, 171 84 Solna, Sverige ISBN 91–7045–471–X ISSN 0346-7821 Tryckt hos CM Gruppen Preface The Nordic Council is an intergovernmental collaborative body for the five countries, Denmark, Finland, Iceland, Norway and Sweden. One of the committees, the Nordic Senior Executive Committee for Occupational Environmental Matters, initiated a project in order to produce criteria documents to be used by the regulatory authorities in the Nordic countries as a scientific basis for the setting of national occupational exposure limits. -
Toxicological Profile for Antimony
ANTIMONY AND COMPOUNDS 11 CHAPTER 2. HEALTH EFFECTS 2.1 INTRODUCTION The primary purpose of this chapter is to provide public health officials, physicians, toxicologists, and other interested individuals and groups with an overall perspective on the toxicology of antimony. It contains descriptions and evaluations of toxicological studies and epidemiological investigations and provides conclusions, where possible, on the relevance of toxicity and toxicokinetic data to public health. When available, mechanisms of action are discussed along with the health effects data; toxicokinetic mechanistic data are discussed in Section 3.1. A glossary and list of acronyms, abbreviations, and symbols can be found at the end of this profile. To help public health professionals and others address the needs of persons living or working near hazardous waste sites, the information in this section is organized by health effect. These data are discussed in terms of route of exposure (inhalation, oral, and dermal) and three exposure periods: acute (≤14 days), intermediate (15–364 days), and chronic (≥365 days). As discussed in Appendix B, a literature search was conducted to identify relevant studies examining health effect endpoints. Figure 2-1 provides an overview of the database of studies in humans or experimental animals included in this chapter of the profile. These studies evaluate the potential health effects associated with inhalation, oral, or dermal exposure to antimony, but may not be inclusive of the entire body of literature. A systematic review of the scientific evidence of the health effects associated with exposure to antimony was also conducted; the results of this review are presented in Appendix C. -
FLAME RETARDANTS in PRINTED CIRCUIT BOARDS Chapter 3
FLAME RETARDANTS IN PRINTED CIRCUIT BOARDS Chapter 3 FINAL REPORT August 2015 EPA Publication 744-R-15-001 3 Chemical Flame Retardants for FR-4 Laminates This chapter summarizes the general characteristics of flame retardants and associated mechanisms of flame retardancy. The flame-retardant chemicals currently used in printed circuit boards (PCBs) are also briefly introduced, with more detailed information about their potential exposure pathways, toxicity, and life-cycle considerations presented in later chapters. 3.1 General Characteristics of Flame-Retardant Chemicals Fire occurs in three stages: (a) thermal decomposition, where the solid, or condensed phase, breaks down into gaseous decomposition products as a result of heat, (b) combustion chain reactions in the gas phase, where thermal decomposition products react with an oxidant (usually air) and generate more combustion products, which can then propagate the fire and release heat, and (c) transfer of the heat generated from the combustion process back to the condensed phase to continue the thermal decomposition process (Hirschler, 1992; Beyler and Hirschler, 2002). In general, flame retardants decrease the likelihood of a fire occurring and/or decrease the undesirable consequences of a fire (Lyons, 1970; Cullis and Hirschler, 1981). The simplest way, in theory, of preventing polymer combustion is to design the polymer so that it is thermally very stable. Thermally stable polymers are less likely to thermally degrade, which prevents combustion from initiating. However, thermally stable polymers are not typically used due to cost and/or other performance issues such as mechanical and electrical properties incompatible with end-use needs for the finished part/item. -
Antimony Trioxide [CAS No. 1309-64-4]
Antimony Trioxide [CAS No. 1309-64-4] Brief Review of Toxicological Literature Prepared for National Toxicology Program (NTP) National Institute of Environmental Health Sciences (NIEHS) National Institutes of Health U.S. Department of Health and Human Services Contract No. N01-ES-35515 Project Officer: Scott A. Masten, Ph.D. NTP/NIEHS Research Triangle Park, North Carolina Prepared by Integrated Laboratory Systems, Inc. Research Triangle Park, North Carolina July 2005 Chemical Name: Antimony Trioxide CAS RN: 1309-64-4 Formula: Sb2O3 Basis for Nomination: Antimony trioxide was nominated by the National Institute of Environmental Health Sciences for chronic toxicity, cardiotoxicity and carcinogenicity studies due to the potential for substantial human exposure in occupational settings and lack of adequate two-year exposure carcinogenicity studies. Additional studies of antimony trioxide are of interest, in lieu of studies with antimony trisulfide or another antimony compound, considering the higher volume of use and magnitude of human exposure, and the lack of two- year exposure carcinogenicity studies for any antimony compound by any route of administration. Antimony trisulfide was nominated to the NTP by the National Cancer Institute in 2002 for carcinogenicity studies (http://ntp.niehs.nih.gov/ntpweb/index.cfm?objectid=25BEBA08-BDB7-CEBA- FC56EAD78615ADCF). Subsequent to the nomination review process, the NTP concluded that antimony trisulfide should not be studied further at this time for the following reasons: 1) antimony trisulfide does not appear to represent a major form of antimony to which humans are exposed; 2) carcinogenicity studies of antimony trisulfide is unlikely to lead to a sufficient understanding of the carcinogenicity hazard for antimony compounds as a group; and 3) there is concern regarding the safe handling of pure antimony trisulfide in experimental settings due to its flammable/combustible nature. -
United States Patent (19) [11] 3,945,974 Schwarcz Et Al
United States Patent (19) [11] 3,945,974 Schwarcz et al. (45) Mar. 23, 1976 54 SMOKE SUPPRESSANTS FOR 2,855,266 l Of 1958 James .............................. 260/45.75 2,948,638 8/1960 Baird............................... 260/45.75 HALOGEN-CONTAINING PLASTIC 3,202,567 8/1965 Muri et al. ...................... 106/15 FP COMPOSITIONS 3,705,128 12/1972 Knowles........................... 260/45.75 75) Inventors: Joseph Schwarcz, Highland Park; 3,766, 57 10/1973 Parts................................ 260/45.75 Bernard Engelbart, Trenton; 3,770,577 1 1/1973 Humpbrey....................... 260/45.75 Edward L. White, Freehold, all of N.J. OTHER PUBLICATIONS 73 Assignee: NL Industries, Inc., New York, Journal of the American Chemical Society Vol. 61, N.Y. No. 12 pp. 3241 to 3244 Dec. 19, 1939. (22 Filed: Dec. 20, 1973 21) Appl. No.: 426,492 Primary Examiner-V. P. Hoke 52 U.S. C.260/31.8 R; 260/45.7 R; 260/45.75 W; 57 ABSTRACT 260/45.75 B (5) Int. Cl.............................................. C08J 3/20 Zinc is added to a halogen-containing plastic composi 58 Field of Search. 260/45.75 R, 45.7 R, 45.75 B, tion with or without a flame retardant additive to 260/45.75 W, 45.75 K, 29. R serve as a smoke suppressant during combustion of the plastic. (56) References Cited UNITED STATES PATENTS 16 Claims, No Drawings 2,772, 59 l/1956 Elliott............................. 260/45.75 3,945,974 2 tions and in particular plasticized polyvinyl chloride SMOKE SUPPRESSANTS FOR include zinc dust, zinc oxide, zinc carbonate, normal HALOGEN-CONTAINING PLASTC zinc -
Chemical Names and CAS Numbers Final
Chemical Abstract Chemical Formula Chemical Name Service (CAS) Number C3H8O 1‐propanol C4H7BrO2 2‐bromobutyric acid 80‐58‐0 GeH3COOH 2‐germaacetic acid C4H10 2‐methylpropane 75‐28‐5 C3H8O 2‐propanol 67‐63‐0 C6H10O3 4‐acetylbutyric acid 448671 C4H7BrO2 4‐bromobutyric acid 2623‐87‐2 CH3CHO acetaldehyde CH3CONH2 acetamide C8H9NO2 acetaminophen 103‐90‐2 − C2H3O2 acetate ion − CH3COO acetate ion C2H4O2 acetic acid 64‐19‐7 CH3COOH acetic acid (CH3)2CO acetone CH3COCl acetyl chloride C2H2 acetylene 74‐86‐2 HCCH acetylene C9H8O4 acetylsalicylic acid 50‐78‐2 H2C(CH)CN acrylonitrile C3H7NO2 Ala C3H7NO2 alanine 56‐41‐7 NaAlSi3O3 albite AlSb aluminium antimonide 25152‐52‐7 AlAs aluminium arsenide 22831‐42‐1 AlBO2 aluminium borate 61279‐70‐7 AlBO aluminium boron oxide 12041‐48‐4 AlBr3 aluminium bromide 7727‐15‐3 AlBr3•6H2O aluminium bromide hexahydrate 2149397 AlCl4Cs aluminium caesium tetrachloride 17992‐03‐9 AlCl3 aluminium chloride (anhydrous) 7446‐70‐0 AlCl3•6H2O aluminium chloride hexahydrate 7784‐13‐6 AlClO aluminium chloride oxide 13596‐11‐7 AlB2 aluminium diboride 12041‐50‐8 AlF2 aluminium difluoride 13569‐23‐8 AlF2O aluminium difluoride oxide 38344‐66‐0 AlB12 aluminium dodecaboride 12041‐54‐2 Al2F6 aluminium fluoride 17949‐86‐9 AlF3 aluminium fluoride 7784‐18‐1 Al(CHO2)3 aluminium formate 7360‐53‐4 1 of 75 Chemical Abstract Chemical Formula Chemical Name Service (CAS) Number Al(OH)3 aluminium hydroxide 21645‐51‐2 Al2I6 aluminium iodide 18898‐35‐6 AlI3 aluminium iodide 7784‐23‐8 AlBr aluminium monobromide 22359‐97‐3 AlCl aluminium monochloride