TOXICOLOGICAL PROFILE for CARBON Dlsulflde

Total Page:16

File Type:pdf, Size:1020Kb

Load more

TOXICOLOGICAL PROFILE FOR CARBON DlSULFlDE U.S. DEPARTMENT OF HEALTH AND HUMAN SERVICES Public Health Service Agency for Toxic Substances and Disease Registry August 1996 CARBON DISULFIDE ii DISCLAIMER The use of company or product name(s) is for identification only and does not imply endorsement by the Agency for Toxic Substances and Disease Registry. CARBON DISULFIDE iii UPDATE STATEMENT A Toxicological Profile for Carbon Disulfide was released in September 1992. This edition supersedes any previously released draft or final profile. Toxicological profiles are revised and republished as necessary, but no less than once every three years. For information regarding the update status of previously released profiles, contact ATSDR at: Agency for Toxic Substances and Disease Registry Division of Toxicology/Toxicology Information Branch 1600 Clifton Road NE, E-29 Atlanta, Georgia 30333 vi *Legislative Background The toxicological profiles are developed in response to the Superfund Amendments and Reauthorization Act (SARA) of 1986 (Public Law 99-499) which amended the Comprehensive Environmental Response, Compensation, and Liability Act of 1980 (CERCLA or Superfund). This public law directed ATSDR to prepare toxicological profiles for hazardous substances most commonly found at facilities on the CERCLA National Priorities List and that pose the most significant potential threat to human health, as determined by ATSDR and the EPA. The availability of the revised priority list of 275 hazardous substances was announced in the Federal Register on April 29,1996 (61 FR 18744). For prior versions of the list of substances, see Federal Register notices dated April 17,1987 (52 FR 12866); October 20, 1988 (53 FR 41280); October 26,1989 (54 FR 43619); October 17,1990 (55 FR 42067); October 17, 1991 (56 FR 52166); October 28,1992 (57 FR 48801); and February 28,1994 (59 FR 9486). Section 104(I)(3) of CERCLA, as amended, directs the Administrator of ATSDR to prepare a toxicological profile for each substance on the list. CARBON DISULFIDE vii CONTRIBUTORS CHEMICAL MANAGER(S)/AUTHOR(S): Henry Abadin, MSPH ATSDR, Division of Toxicology, Atlanta, GA John J. Liccione, Ph.D. Sciences International, Inc., Alexandria, VA THE PROFILE HAS UNDERGONE THE FOLLOWING ATSDR INTERNAL REVIEWS: 1. Green Border Review. Green Border review assures the consistency with ATSDR policy. 2. Health Effects Review. The Health Effects Review Committee examines the health effects chapter of each profile for consistency and accuracy in interpreting health effects and classifying end points. 3. Minimal Risk Level Review. The Minimal Risk Level Workgroup considers issues relevant to substance-specific minimal risk levels (MRLs), reviews the health effects database of each profile, and makes recommendations for derivation of MRLs. CARBON DISULFIDE ix PEER REVIEW A peer review panel was assembled for carbon disulfide. The panel consisted of the following members: 1. Dr. Henry Peters, Professor of Neurology, University of Wisconsin, Madison, WI 2. Dr. Shane Que Hee, Professor of Environmental Health Sciences, UCLA School of Public Health, Los Angeles, CA 3. Dr. Robert Rubin, Professor of Toxicology, Environmental Health Sciences, Johns Hopkins School of Hygiene and Public Health, Baltimore, MD These experts collectively have knowledge of carbon disulfide’s physical and chemical properties, toxicokinetics, key health end points, mechanisms of action, human and animal exposure, and quantification of risk to humans. All reviewers were selected in conformity with the conditions for peer review specified in Section 104(i)(l3) of the Comprehensive Environmental Response, Compensation, and Liability Act, as amended. Scientists from the Agency for Toxic Substances and Disease Registry (ATSDR) have reviewed the peer reviewers’ comments and determined which comments will be included in the profile. A listing of the peer reviewers’ comments not incorporated in the profile, with a brief explanation of the rationale for their exclusion, exists as part of the administrative record for this compound. A list of databases reviewed and a list of unpublished documents cited are also included in the administrative record. The citation of the peer review panel should not be understood to imply its approval of the profile’s final content. The responsibility for the content of this profile lies with the ATSDR. CARBON DISULFIDE 1 1. PUBLIC HEALTH STATEMENT This public health statement tells you about carbon disulfide and the effects of exposure. The Environmental Protection Agency (EPA) identifies the most serious hazardous waste sites in the nation. These sites make up the National Priorities List (NPL) and are the sites targeted for long-term federal cleanup. Carbon disulfide has been found in at least 200 of the 1,430 current or former NPL sites. However, it’s unknown how many NPL sites have been evaluated for this substance. As more sites are evaluated, the sites with carbon disulfide may increase. This information is important because exposure to this substance may harm you and because these sites may be sources of exposure. When a substance is released from a large area, such as an industrial plant, or from a container, such as a drum or bottle, it enters the environment. This release does not always lead to exposure. You can be exposed to a substance only when you come into contact with it. You may be exposed by breathing, eating, or drinking the substances or by skin contact. If you are exposed to carbon disulfide, many factors determine whether you’ll be harmed. These factors include the dose (how much), the duration (how long), and how you come in contact with it. You must also consider the other chemicals you’re exposed to and your age, sex, diet, family traits, life-style, and state of health. 1.1 WHAT IS CARBON DISULFIDE? Pure carbon disulfide is a colorless liquid with a pleasant odor that smells sweet, The impure carbon disulfide that is usually used in most industrial processes, however, is a yellowish liquid with an unpleasant odor like that of rotting radishes. Carbon disulfide evaporates at room temperature, and the vapor is more than twice as heavy as air. Carbon disulfide easily explodes in air and also catches fire very easily. CARBON DISULFIDE 2 1. PUBLIC HEALTH STATEMENT In nature, small amounts of carbon disulfide are found in gases released to the earth’s surface, for example, in volcanic eruptions or over marshes. Microorganisms in the soil can also produce gas containing carbon disulfide. Commercial carbon disulfide is made by combining carbon and sulfur at very high temperatures. Several industries use carbon disulfide as a raw material to make such things as rayon, cellophane, and carbon tetrachloride. Currently, the largest user of this chemical is the viscose rayon industry. Carbon disulfide is also used to dissolve rubber to produce tires and as a raw material to make some pesticides. See Chapters 3, 4, and 5 for more information on the chemical and physical properties, use, and environmental fate of carbon disulfide. 1.2 WHAT HAPPENS TO CARBON DlSULFlDE WHEN IT ENTERS THE ENVIRONMENT? Carbon disulfide evaporates rapidly when released to the environment. The amount of carbon disulfide released into the air through natural processes is difficult to judge because it is in such small amounts in nature. This also makes it hard to monitor carbon disulfide and to explain how it behaves when it comes into contact with other compounds. Most carbon disulfide in the air and in surface water is from manufacturing and processing activities. However, it is found naturally in coastal and ocean waters. Carbon disulfide has also been found in the groundwater and soil at some EPA research sites around the country, but the number of research sites that have carbon disulfide is small. Once released to the environment, carbon disulfide moves quickly to the air. Once in the air, carbon disulfide stays close to the ground because it is heavier than the surrounding air. It is estimated that carbon disulfide will break down into simpler components after approximately 12 days. Carbon disulfide moves through soils fairly quickly. Carbon disulfide accidentally released to soils normally evaporates rapidly. However, since carbon disulfide does not bind tightly to soils, the amount that does not evaporate can easily move down through the soil into groundwater. Since it is very mobile, it is not likely to stay in the soil long enough to be broken down. It does not remain very long in water either because it evaporates within minutes. However, if dissolved in water, it is relatively stable and is not easily broken down. CARBON DlSULFlDE 3 1. PUBLIC HEALTH STATEMENT It is estimated that carbon disulfide is not taken up in significant amounts by the organisms living in water. 1.3 HOW MIGHT I BE EXPOSED TO CARBON DISULFIDE? Carbon disulfide can enter your body if you breath air, drink water, or eat foods that contain it. You can also be exposed by skin contact with soil, water, or other substances that contain it. Oceans are a major natural source. The amount of carbon disulfide found in the air from natural sources such as volcanoes is so low that good measurements are not available from many areas. One measurement shows that carbon disulfide produced by marshes contributes less than 8% of the sulfur in the upper atmosphere. Small amounts of carbon disulfide can enter the air by evaporation and as a by-product of several manufacturing processes. It is not clear how long carbon disulfide stays in the air. Estimates range from 1 to 10 weeks. The people most often exposed to carbon disulfide are workers in plants that use carbon disulfide in their manufacturing processes. The main way they are exposed is through the air, and secondarily the skin. Carbon disulfide has also been found in small amounts in some drinking water in the United States. Chapter 5 contains more information on how you might be exposed to carbon disulfide.
Recommended publications
  • Chemistry Department 32.Pdf (10.36Mb)

    Chemistry Department 32.Pdf (10.36Mb)

    THE FABRICATION OF NANOMETRIC METAL SULFIDES FROM XANTHATE PRECURSORS By ALAN PIQUETTE Bachelor of Arts Western State College of Colorado Gunnison, Colorado 2002 Submitted to the Faculty of the Graduate College of the Oklahoma State University In partial fulfillment of The requirements for The Degree of DOCTOR OF PHILOSOPHY December, 2007 THE FABRICATION OF NANOMETRIC METAL SULFIDES FROM XANTHATE PRECURSORS Thesis Approved: _______________ __Allen Apblett___ ______________ Thesis Advisor ________________ Nicholas Materer_____ __________ _____________ __LeGrande Slaughter___ __________ _______________ ____Jim Smay___ _______________ _____________ __A. Gordon Emslie___ ____________ Dean of the Graduate College ACKNOWLEDGEMENTS It is with my utmost sincere appreciation that I acknowledge my thesis advisor, Dr. Allen W. Apblett, for his support, guidance, and motivation. He provided a research environment that was both friendly and challenging, which made my years in his group enjoyable and rewarding. His broad range of knowledge was something of which I was happy to take advantage. His dedication to teaching and research is something that will be a positive influence on me for the rest of my scientific career. I would like to express gratitude to my committee members: Dr. Nicholas Materer, Dr. LeGrande Slaughter, and Dr. Jim Smay, for their assistance, advice, guidance, and support throughout the years. I am deeply grateful to all my colleagues and friends in the chemistry department. I would specifically like to thank Sulaiman Al-Fadul, Mohammed Al-Hazmi, Zeid Al- Othmann, Mohamed Chehbouni, Satish Kuriyavar, and Tarek Trad for showing me the ropes, for their valuable discussions, continuous encouragement, and for all the help they extended during the course of my stay in the Apblett Group.
  • Activated Carbon, Biochar and Charcoal: Linkages and Synergies Across Pyrogenic Carbon’S Abcs

    Activated Carbon, Biochar and Charcoal: Linkages and Synergies Across Pyrogenic Carbon’S Abcs

    water Review Activated Carbon, Biochar and Charcoal: Linkages and Synergies across Pyrogenic Carbon’s ABCs Nikolas Hagemann 1,* ID , Kurt Spokas 2 ID , Hans-Peter Schmidt 3 ID , Ralf Kägi 4, Marc Anton Böhler 5 and Thomas D. Bucheli 1 1 Agroscope, Environmental Analytics, Reckenholzstrasse 191, CH-8046 Zurich, Switzerland; [email protected] 2 United States Department of Agriculture, Agricultural Research Service, Soil and Water Management Unit, St. Paul, MN 55108, USA; [email protected] 3 Ithaka Institute, Ancienne Eglise 9, CH-1974 Arbaz, Switzerland; [email protected] 4 Eawag, Swiss Federal Institute of Aquatic Science and Technology, Department Process Engineering, Überlandstrasse 133, CH-8600 Dübendorf, Switzerland; [email protected] 5 Eawag, Swiss Federal Institute of Aquatic Science and Technology, Application and Development, Department Process Engineering, Überlandstrasse 133, CH-8600 Dübendorf, Switzerland; [email protected] * Correspondence: [email protected]; Tel.: +41-58-462-1074 Received: 11 January 2018; Accepted: 1 February 2018; Published: 9 February 2018 Abstract: Biochar and activated carbon, both carbonaceous pyrogenic materials, are important products for environmental technology and intensively studied for a multitude of purposes. A strict distinction between these materials is not always possible, and also a generally accepted terminology is lacking. However, research on both materials is increasingly overlapping: sorption and remediation are the domain of activated carbon, which nowadays is also addressed by studies on biochar. Thus, awareness of both fields of research and knowledge about the distinction of biochar and activated carbon is necessary for designing novel research on pyrogenic carbonaceous materials. Here, we describe the dividing ranges and common grounds of biochar, activated carbon and other pyrogenic carbonaceous materials such as charcoal based on their history, definition and production technologies.
  • Toxicity Reduction Evaluation Guidance for Municipal Wastewater Treatment Plants EPA/833B-99/002 August 1999

    Toxicity Reduction Evaluation Guidance for Municipal Wastewater Treatment Plants EPA/833B-99/002 August 1999

    United States Office of Wastewater EPA/833B-99/002 Environmental Protection Management August 1999 Agency Washington DC 20460 Toxicity Reduction Evaluation Guidance for Municipal Wastewater Treatment Plants EPA/833B-99/002 August 1999 Toxicity Reduction Evaluation Guidance for Municipal Wastewater Treatment Plants Office of Wastewater Management U.S. Environmental Protection Agency Washington, D.C. 20460 Notice and Disclaimer The U.S. Environmental Protection Agency, through its Office of Water, has funded, managed, and collaborated in the development of this guidance, which was prepared under order 7W-1235-NASX to Aquatic Sciences Consulting; order 5W-2260-NASA to EA Engineering, Science and Technology, Inc.; and contracts 68-03-3431, 68-C8-002, and 68-C2-0102 to Parsons Engineering Science, Inc. It has been subjected to the Agency's peer and administrative review and has been approved for publication. The statements in this document are intended solely as guidance. This document is not intended, nor can it be relied on, to create any rights enforceable by any party in litigation with the United States. EPA and State officials may decide to follow the guidance provided in this document, or to act at variance with the guidance, based on an analysis of site-specific circumstances. This guidance may be revised without public notice to reflect changes in EPA policy. ii Foreword This document is intended to provide guidance to permittees, permit writers, and consultants on the general approach and procedures for conducting toxicity reduction evaluations (TREs) at municipal wastewater treatment plants. TREs are important tools for Publicly Owned Treatment Works (POTWs) to use to identify and reduce or eliminate toxicity in a wastewater discharge.
  • United States Patent (113,607,865

    United States Patent (113,607,865

    United States Patent (113,607,865 (72) Inventors John Dyer (56) References Cited Media; UNITED STATES PATENTS Lyle H. Phifer, West Chester, both of Pa. 2,694,723 l l 11954 Schramm ..................... 260/455 B 2l Appl. No. 732,551 2,761,247 9/1956 Meadows.... a 260/216 22 Filed May 28, 1968 2,825,655 3/1958 Meadows..................... 260/216 45) Patented Sept. 21, 1971 2,910,466 101959 Watt............................. 260/216 73) Assignee FMC Corporation Philadelphia, Pa. 3.141023,103,507 9/19637/1964 O'Boyle...Knoevenagel. 260/234 Primary Examiner-Lewis Gotts (54) PREPARATION OFXANTHATES Assistant Examiner-Johnnie R. Brown 10 Claims, No Drawings Attorneys-Thomas R. O'Malley, George F. Mueller and Robert G. Hoffmann 52) U.S.C........................................................ 260/234 R, 260/26, 260/455 B 51 int. Cl......................................................... C07c69132 ABSTRACT: A method of forming alcohol xanthates utilizing 50 Field of Search............................................ 260/455 B, a transXanthation reaction between an alcohol xanthate and 234,216 an alcohol, is disclosed herein. 3,607,865 PREPARATION OFXANTHATES erythritol Alcohol xanthic acids and their derivatives are known to be sorbital useful for a variety of applications including mineral flotation glucose agents, sulfidizing agents, rubber vulcanization accelerators, mannitol adhesives and as intermediates in the preparation of shaped 2-methoxyethanol articles, for example, regenerated cellulose fibers and films. 2-ethoxyethanol In general, alcohol xanthates have been derived by reacting 2-butoxyethanol carbon disulfide with simple and complex alcohols under al diethyleneglycol ethylether kaline conditions. Reactions of this type have been known for polyethylene glycols many years and may be seen, for example, in many prior U.S.
  • An Improved Method for BTEX Extraction From

    An Improved Method for BTEX Extraction From

    Analytical Methods Accepted Manuscript This is an Accepted Manuscript, which has been through the Royal Society of Chemistry peer review process and has been accepted for publication. Accepted Manuscripts are published online shortly after acceptance, before technical editing, formatting and proof reading. Using this free service, authors can make their results available to the community, in citable form, before we publish the edited article. We will replace this Accepted Manuscript with the edited and formatted Advance Article as soon as it is available. You can find more information about Accepted Manuscripts in the Information for Authors. Please note that technical editing may introduce minor changes to the text and/or graphics, which may alter content. The journal’s standard Terms & Conditions and the Ethical guidelines still apply. In no event shall the Royal Society of Chemistry be held responsible for any errors or omissions in this Accepted Manuscript or any consequences arising from the use of any information it contains. www.rsc.org/methods Page 1 of 6 Analytical Methods 1 2 Analytical Methods RSC Publishing 3 4 5 TECHNICAL NOTE 6 7 8 9 An improved method for BTEX extraction from 10 charcoal 11 Cite this: DOI: 10.1039/x0xx00000x 12 13 Raffaele Cucciniello a, Antonio Proto a,*, Federico Rossi a, Nadia 14 b c 15 Marchettini , Oriana Motta Received 00th January 2015, 16 Accepted 00th January 2015 17 Abstract In this paper we propose a simple procedure for the extraction of BTEX (benzene, 18 DOI: 10.1039/x0xx00000x toluene, ethylbenzene and xylenes) from activated charcoal. For this purpose synthetic samples 19 www.rsc.org/ were prepared in laboratory and real samples were collected in a polluted environment using 20 21 passive sampling.
  • 1997-11-12 Carbon Disulfide As Federal Hazardous Air Pollutant

    1997-11-12 Carbon Disulfide As Federal Hazardous Air Pollutant

    CARBON DISULFIDE Carbon disulfide is a federal hazardous air pollutant and was identified as a toxic air contaminant in April 1993 under AB 2728. CAS Registry Number: 75-15-0 CS2 Molecular Formula: CS2 Carbon disulfide is a highly refractive, mobile, and very flammable liquid. The purest distillates have a sweet odor. However, the usual commercial and reagent grades of carbon disulfide are foul smelling. It burns with a blue flame to form carbon dioxide and sulfur dioxide. Liquid carbon disulfide will attack some forms of plastics, rubber, and coatings but is non- corrosive to most commercial structural materials at ordinary temperatures. It is miscible in water, alcohol, oils, chloroform, and ether (Merck, 1989). Physical Properties of Carbon Disulfide Synonyms: carbon bisulfide; carbon disulphide; carbon sulfide; sulphocarbonic anhydride; sulphuret of carbon; dithiocarbonic anhydride Molecular Weight: 76.14 Boiling Point: 46.5 oC Melting Point: -111.5 oC Vapor Density: 2.67 (air =1) Flash Point: -30 oC (closed cup) Density/Specific Gravity: 1.2632 at 20/4 oC (water = 1) Critical Temperature: 280 oC Vapor Pressure: 297 mm Hg at 20 oC Log Octanol/Water Partition Coefficient: 1.70 - 4.16 Conversion Factor: 1 ppm = 3.11 mg/m3 (Howard, 1990; HSDB, 1991; Merck, 1989; U.S. EPA, 1994a) SOURCES AND EMISSIONS A. Sources Carbon disulfide is used in the preparation of rayon viscose fibers, and as a solvent for lipids, phosphorus, sulfur, selenium, bromine, iodine, rubber, resins, and waxes (Proctor et al, 1991). Carbon disulfide is also used in the manufacture of carbon tetrachloride, cellophane, flotation Toxic Air Contaminant Identification List Summaries - ARB/SSD/SES September 1997 193 Carbon Disulfide agents, xanthogenates, and numerous other chemicals (HSDB, 1991; Sax, 1987).
  • Carbonyl Sulfide, Dimethyl Sulfide and Carbon Disulfide In

    Carbonyl Sulfide, Dimethyl Sulfide and Carbon Disulfide In

    Atmospheric Environment 44 (2010) 3805e3813 Contents lists available at ScienceDirect Atmospheric Environment journal homepage: www.elsevier.com/locate/atmosenv Carbonyl sulfide, dimethyl sulfide and carbon disulfide in the Pearl River Delta of southern China: Impact of anthropogenic and biogenic sources H. Guo a,*, I.J. Simpson b, A.J. Ding c,T.Wanga, S.M. Saunders d, T.J. Wang c, H.R. Cheng a, B. Barletta b, S. Meinardi b, D.R. Blake b, F.S. Rowland b a Department of Civil and Structural Engineering, Hong Kong Polytechnic University, Hong Kong b Department of Chemistry, University of California at Irvine, Irvine, USA c School of Atmospheric Sciences, Nanjing University, China d School of Biomedical, Biomolecular and Chemical Sciences, University of Western Australia, Perth, Australia article info abstract Article history: Reduced sulfur compounds (RSCs) such as carbonyl sulfide (OCS), dimethyl sulfide (DMS) and carbon Received 28 October 2009 disulfide (CS2) impact radiative forcing, ozone depletion, and acid rain. Although Asia is a large source of Received in revised form these compounds, until now a long-term study of their emission patterns has not been carried out. Here 19 June 2010 we analyze 16 months of RSC data measured at a polluted rural/coastal site in the greater Pearl River Accepted 22 June 2010 Delta (PRD) of southern China. A total of 188 canister air samples were collected from August 2001 to December 2002. The OCS and CS2 mixing ratios within these samples were higher in autumn/winter and Keywords: lower in summer due to the influence of Asian monsoon circulations.
  • Activated Carbon from the Graphite with Increased Rate Capability for the Potassium Ion Battery Zhixin Tai University of Wollongong, Zt525@Uowmail.Edu.Au

    Activated Carbon from the Graphite with Increased Rate Capability for the Potassium Ion Battery Zhixin Tai University of Wollongong, [email protected]

    University of Wollongong Research Online Australian Institute for Innovative Materials - Papers Australian Institute for Innovative Materials 2017 Activated carbon from the graphite with increased rate capability for the potassium ion battery Zhixin Tai University of Wollongong, [email protected] Qing Zhang University of Wollongong, [email protected] Yajie Liu University of Wollongong, [email protected] Hua-Kun Liu University of Wollongong, [email protected] Shi Xue Dou University of Wollongong, [email protected] Publication Details Tai, Z., Zhang, Q., Liu, Y., Liu, H. & Dou, S. (2017). Activated carbon from the graphite with increased rate capability for the potassium ion battery. Carbon, 123 54-61. Research Online is the open access institutional repository for the University of Wollongong. For further information contact the UOW Library: [email protected] Activated carbon from the graphite with increased rate capability for the potassium ion battery Abstract Activated carbon has been synthesized by a high-temperature annealing route using graphite as carbon source and potassium hydroxide as the etching agent. Many nanosized carbon sheets formed on the particles could be of benefit for ar pid intercalation/de-intercalation of potassium ions. Moreover, the d-spacing in the (100) crystal planes of the as-prepared active carbon is enlarged to 0.335 nm, even some formed carbon nanosheets can reach 0.358 nm, and the diffusion coefficient of K ion is also improved by 7 times as well. The as-prepared activated carbon electrode can deliver a high reversible capacity of 100 mAh g ¿1 after 100 cycles (at a high current density of 0.2 A g ¿1 ), and exhibits increased rate performance.
  • Single-Dose Activated Charcoal

    Single-Dose Activated Charcoal

    Clinical Toxicology ISSN: 1556-3650 (Print) 1556-9519 (Online) Journal homepage: http://www.tandfonline.com/loi/ictx20 Position Paper: Single-Dose Activated Charcoal American Academy of Clinical Toxicology & European Association of Poisons Centres and Clinical Toxicologists To cite this article: American Academy of Clinical Toxicology & European Association of Poisons Centres and Clinical Toxicologists (2005) Position Paper: Single-Dose Activated Charcoal, Clinical Toxicology, 43:2, 61-87, DOI: 10.1081/CLT-51867 To link to this article: http://dx.doi.org/10.1081/CLT-51867 Published online: 07 Oct 2008. Submit your article to this journal Article views: 655 View related articles Citing articles: 2 View citing articles Full Terms & Conditions of access and use can be found at http://www.tandfonline.com/action/journalInformation?journalCode=ictx20 Download by: [UPSTATE Medical University Health Sciences Library] Date: 29 May 2017, At: 09:32 Clinical Toxicology, 43:61–87, 2005 Copyright D Taylor & Francis Inc. ISSN: 0731-3810 print / 1097-9875 online DOI: 10.1081/CLT-200051867 POSITION PAPER Position Paper: Single-Dose Activated Charcoal# American Academy of Clinical Toxicology and European Association of Poisons Centres and Clinical Toxicologists developing serious complications and who might potentially Single-dose activated charcoal therapy involves the oral benefit, therefore, from gastrointestinal decontamination. administration or instillation by nasogastric tube of an aqueous Single-dose activated charcoal therapy involves the oral preparation of activated charcoal after the ingestion of a poison. administration or instillation by nasogastric tube of an Volunteer studies demonstrate that the effectiveness of activated charcoal decreases with time. Data using at least 50 g of activated aqueous preparation of activated charcoal after the ingestion charcoal, showed a mean reduction in absorption of 47.3%, of a poison.
  • Performance Asymmetric Supercapacitors Stack Based on Nickel Hexacyanoferrate-Derived Ni(OH)

    Performance Asymmetric Supercapacitors Stack Based on Nickel Hexacyanoferrate-Derived Ni(OH)

    www.nature.com/scientificreports OPEN Fabrication of 9.6 V High- performance Asymmetric Supercapacitors Stack Based on Received: 17 August 2018 Accepted: 10 December 2018 Nickel Hexacyanoferrate-derived Published: xx xx xxxx Ni(OH)2 Nanosheets and Bio- derived Activated Carbon Subramani Kaipannan1,2 & Sathish Marappan1,2 Hydrated Ni(OH)2 and activated carbon based electrodes are widely used in electrochemical applications. Here we report the fabrication of symmetric supercapacitors using Ni(OH)2 nanosheets and activated carbon as positive and negative electrodes in aqueous electrolyte, respectively. The asymmetric supercapacitors stack connected in series exhibited a stable device voltage of 9.6 V and delivered a stored high energy and power of 30 mWh and 1632 mW, respectively. The fabricated device shows an excellent electrochemical stability and high retention of 81% initial capacitance after 100,000 charge-discharges cycling at high charging current of 500 mA. The positive electrode material Ni(OH)2 nanosheets was prepared through chemical decomposition of nickel hexacyanoferrate complex. The XRD pattern revealed the high crystalline nature of Ni(OH)2 with an average crystallite size of ~10 nm. The nitrogen adsorption-desorption isotherms of Ni(OH)2 nanosheets indicate the formation of mesoporous Ni(OH)2 nanosheets. The chemical synthesis of Ni(OH)2 results the formation of hierarchical nanosheets that are randomly oriented which was confrmed by FE-SEM and HR-TEM analysis. The negative electrode, activated porous carbon (OPAA-700) was obtained from orange peel waste. The electrochemical properties of Ni(OH)2 nanosheets and OPAA-700 were studied and exhibit a high specifc capacity of 1126 C/g and high specifc capacitance of 311 F/g at current density of 2 A/g, respectively.
  • Research and Development

    Research and Development

    EPA-600/R-00-083 September 2000 Research and Development PERFORMANCE AND COST OF MERCURY EMISSION CONTROL TECHNOLOGY APPLICATIONS ON ELECTRIC UTILITY BOILERS Prepared for Office of Air and Radiation Prepared by National Risk Management Research Laboratory Research Triangle Park, NC 27711 FOREWORD The U. S. Environmental Protection Agency is charged by Congress with pro- tecting the Nation's land, air, and water resources. Under a mandate of national environmental laws, the Agency strives to formulate and implement actions lead- ing to a compatible balance between human activities and the ability of natural systems to support and nurture life. To meet this mandate, EPA's research program is providing data and technical support for solving environmental pro- blems today and building a science knowledge base necessary to manage our eco- logical resources wisely, understand how pollutants affect our health, and pre- vent or reduce environmental risks in the future. The National Risk Management Research Laboratory is the Agency's center for investigation of technological and management approaches for reducing risks from threats to human health and the environment. The focus of the Laboratory's research program is on methods for the prevention and control of pollution to air, land, water, and subsurface resources, protection of water quality in public water systems; remediation of contaminated sites and-groundwater; and prevention and control of indoor air pollution. The goal of this research effort is to catalyze development and implementation of innovative, cost-effective environmental technologies; develop scientific and engineering information needed by EPA to support regulatory and policy decisions; and provide technical support and infor- mation transfer to ensure effective implementation of environmental regulations and strategies.
  • Structural Modification of Xanthate Collectors to Enhance the Flotation

    Structural Modification of Xanthate Collectors to Enhance the Flotation

    Article pubs.acs.org/IECR Structural Modification of Xanthate Collectors To Enhance the Flotation Selectivity of Chalcopyrite † ‡ † † † Xin Ma, Liuyin Xia, Shuai Wang,*, Hong Zhong,*, and Hui Jia † College of Chemistry and Chemical Engineering, Central South University, Changsha 410083, People’s Republic of China ‡ Surface Science, University of Western Ontario, London, Ontario N6G0J3, Canada *S Supporting Information ABSTRACT: A modified xanthate compound similar to xanthogen formates, S-benzoyl O-isobutyl xanthate (BIBX), was designed by introducing a carbonyl and a benzyl group into the xanthate structure. The preparation, recovery performance, and mechanism of adsorption of this compound to chalcopyrite is discussed. BIBX was synthesized using a one-pot approach with superior efficiency, which has important commercial implications. BIBX’s performance in the recovery of and mechanism of adsorption to chalcopyrite was investigated via flotation tests, adsorption quantity measurements, FTIR spectroscopy, X- ray photoelectron spectroscopy (XPS), and density functional theory (DFT) calculations. The results show that BIBX displays a substantially stronger collecting ability toward chalcopyrite than sodium isobutyl xanthate and O-isopropyl-N- ethylthionocarbamate. Moreover, BIBX displays superior selectivity for chalcopyrite compared to pyrite. The adsorption data indicate that BIBX can be applied under slightly acidic or alkaline conditions. BIBX behaves like a bidentate ligand, bonding with the chalcopyrite copper through the thiol sulfur and carbonyl oxygen atoms. These findings are supported by FTIR and XPS data. DFT calculations predict two distinct adsorption geometries, one with one Cu atom to form a six-membered ring complex and another with two Cu atoms to form an “irregular pentagon”-shaped complex. 1. INTRODUCTION atom.