PROVISIONAL PEER REVIEWED TOXICITY VALUES for DIMETHYLMERCURY (CASRN 593-74-8) Derivation of Subchronic and Chronic Oral Rfds
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Chemical Threat Agents Call Poison Control 24/7 for Treatment Information 1.800.222.1222 Blood Nerve Blister Pulmonary Metals Toxins
CHEMICAL THREAT AGENTS CALL POISON CONTROL 24/7 FOR TREATMENT INFORMATION 1.800.222.1222 BLOOD NERVE BLISTER PULMONARY METALS TOXINS SYMPTOMS SYMPTOMS SYMPTOMS SYMPTOMS SYMPTOMS SYMPTOMS • Vertigo • Diarrhea, diaphoresis • Itching • Upper respiratory tract • Cough • Shock • Tachycardia • Urination • Erythema irritation • Metallic taste • Organ failure • Tachypnea • Miosis • Yellowish blisters • Rhinitis • CNS effects • Cyanosis • Bradycardia, bronchospasm • Flu-like symptoms • Coughing • Shortness of breath • Flu-like symptoms • Emesis • Delayed eye irritation • Choking • Flu-like symptoms • Nonspecific neurological • Lacrimation • Delayed pulmonary edema • Visual disturbances symptoms • Salivation, sweating INDICATIVE LAB TESTS INDICATIVE LAB TESTS INDICATIVE LAB TEST INDICATIVE LAB TESTS INDICATIVE LAB TESTS INDICATIVE LAB TESTS • Increased anion gap • Decreased cholinesterase • Thiodiglycol present in urine • Decreased pO2 • Proteinuria None Available • Metabolic acidosis • Increased anion gap • Decreased pCO2 • Renal assessment • Narrow pO2 difference • Metabolic acidosis • Arterial blood gas between arterial and venous • Chest radiography samples DEFINITIVE TEST DEFINITIVE TEST DEFINITIVE TEST DEFINITIVE TESTS DEFINITIVE TESTS • Blood cyanide levels • Urine nerve agent • Urine blister agent No definitive tests available • Blood metals panel • Urine ricinine metabolites metabolites • Urine metals panel • Urine abrine POTENTIAL AGENTS POTENTIAL AGENTS POTENTIAL AGENTS POTENTIAL AGENTS POTENTIAL AGENTS POTENTIAL AGENTS • Hydrogen Cyanide -
Theoretical Studies of Phenylmercury Carboxylates
TA Theoretical studies of Phenylmercury 2750 carboxylates 2010 This page is intentionally left blank Theoretical studies of Phenylmercury carboxylates Complexation Constants and Gas Phase Photo- Oxidation of Phenylmercurycarboxylates. Yizhen Tang and Claus Jørgen Nielsen CTCC, Department of Chemistry, University of Oslo This page is intentionally left blank Table of Contents Executive Summary ................................................................................................................ 1 1. Quantum chemistry studies on phenylmercurycarboxylates ..................................... 3 2. Results from quantum chemistry ................................................................................... 3 2.1 Structure of phenylmercury(II) carboxylates .............................................................. 4 2.2 Energies of complexation/dissociation ....................................................................... 9 2.3 Vertical excitation energies......................................................................................... 10 2.4 Vertical ionization energies ......................................................................................... 11 2.5 Summary of results from quantum chemistry calculations .................................... 11 3. Atmospheric fate and lifetimes of phenylmercurycarboxylates ............................... 12 3.1 Literature data............................................................................................................... 12 3.2 Estimation of the -
Stability of Dimethylmercury and Related Mercury-Containing Compounds with Respect to Selected Chemical Species Found in Aqueous Environment†
CROATICA CHEMICA ACTA CCACAA, ISSN 0011-1643, e-ISSN 1334-417X Croat. Chem. Acta 86 (4) (2013) 453–462. http://dx.doi.org/10.5562/cca2314 Original Scientific Article Stability of Dimethylmercury and Related Mercury-containing Compounds † with Respect to Selected Chemical Species Found in Aqueous Environment Laimutis Bytautas Department of Chemistry, Rice University, Houston, Texas 77005, USA, Present address: Galveston College, Department of Chemistry, 4015 Avenue Q, Galveston, TX, 77550, USA. (E-mail: [email protected]) RECEIVED JUNE 23, 2013; REVISED OCTOBER 3, 2013; ACCEPTED OCTOBER 4, 2013 Abstract. Dimethylmercury (CH3−Hg−CH3) and other Hg-containing compounds can be found in atmos- pheric and aqueous environments. These substances are highly toxic and pose a serious environmental and health hazard. Therefore, the understanding of chemical processes that affect the stability of these sub- stances is of great interest. The mercury-containing compounds can be detected in atmosphere, as well as soil and aqueous environments where, in addition to water molecules, numerous ionic species are abun- dant. In this study we explore the stability of several small, Hg-containing compounds with respect to wa- + ter molecules, hydronium (H3O ) ions as well as other small molecules/ions using density functional theo- ry and wave function quantum chemistry methods. It is found that the stability of such molecules, most + notably of dimethylmercury, can be strongly affected by the presence of the hydronium H3O ions. Alt- hough the present theoretical study represents gas phase results, it implies that pH level of a solution should be a major factor in determining the degree of abundance for dimethylmercury in aqueous envi- + ronment. -
Results of the Lake Michigan Mass Balance Study: Mercury Data Report
Results of the Lake Michigan Mass Balance Study: Mercury Data Report February 2004 U.S. Environmental Protection Agency Great Lakes National Program Office (G-17J) 77 West Jackson Boulevard Chicago, IL 60604 EPA 905 R-01-012 Results of the Lake Michigan Mass Balance Study: Mercury Data Report Prepared for: US EPA Great Lakes National Program Office 77 West Jackson Boulevard Chicago, Illinois 60604 Prepared by: Harry B. McCarty, Ph.D., Ken Miller, Robert N. Brent, Ph.D., and Judy Schofield DynCorp (a CSC Company) 6101 Stevenson Avenue Alexandria, Virginia 22304 and Ronald Rossmann, Ph.D. US EPA Office of Research and Development Large Lakes Research Station 9311 Groh Road Grosse Ile, Michigan 48138 February 2004 Acknowledgments This report was prepared under the direction of Glenn Warren, Project Officer, USEPA Great Lakes National Program Office; and Louis Blume, Work Assignment Manager and Quality Assurance Officer, USEPA Great Lakes National Program Office (GLNPO). The report was prepared by Harry B. McCarty, Ken Miller, Robert N. Brent, and Judy Schofield, with DynCorp’s Science and Engineering Programs, and Ronald Rossmann, USEPA Large Lakes Research Station, with significant contributions from the LMMB Principal Investigators for mercury and Molly Middlebrook, of DynCorp. GLNPO thanks these investigators and their associates for their technical support in project development and implementation. Ronald Rossmann wishes to thank Theresa Uscinowicz for assistance with collection, preparation, and analysis of the samples; special thanks to staff of the NOAA Great Lakes Environmental Research Laboratory, University of Wisconsin-Milwaukee Great Lakes Water Institute Center for Great Lakes Studies, USEPA Great Lakes National Program, and USEPA Mid-Continent Ecology Division for collection of the samples. -
Notes from Rao 2/13/2007 2:07:37 PM
Environmental Assessment of Sediments and Water in Bayou Grande, Pensacola, FL. Dr. Carl J. Mohrherr Center for Environmental Diagnostics and Bioremediation University of West Florida Dr. Johan Liebens Department of Environmental Studies University of West Florida Dr. K. Ranga Rao Center for Environmental Diagnostics and Bioremediation University of West Florida June 26, 2008 FOREWORD This study is a component of the "Assessment of Environmental Pollution and Community Health in Northwest Florida" supported by a USEPA Cooperative Agreement award X-9745502 to The University of West Florida (Project Director: Dr. K. Ranga Rao). The contents of this report are solely the responsibility of the authors and do not necessarily represent the official views of the USEPA. The study was undertaken because of the increasing concern for environmental pollution and potential impacts on human health in Northwest Florida. It was designed to assess environmental impacts of toxic pollutants in Bayou Grande. Kristal Flanders managed the spatial databases for the project and drafted the maps. Her assistance has been invaluable. Chris Carlton-Franco, Brandon Jarvis, Guy Allard, and Danielle Peterson helped with the fieldwork and some laboratory procedures. Creative Commons License This work is licensed under a Creative Commons Attribution- NonCommercial- NoDerivatives 4.0 International License. i TABLE OF CONTENTS I INTRODUCTION........................................................................................................... 1 II STUDY AREA............................................................................................................. -
Emea Public Statement on Thiomersal in Vaccines for Human Use – Recent Evidence Supports Safety of Thiomersal-Containing Vaccines
The European Agency for the Evaluation of Medicinal Products Pre-authorisation evaluation of medicines for human use London, 24 March 2004 Doc. Ref: EMEA/CPMP/VEG/1194/04/Adopted EMEA PUBLIC STATEMENT ON THIOMERSAL IN VACCINES FOR HUMAN USE – RECENT EVIDENCE SUPPORTS SAFETY OF THIOMERSAL-CONTAINING VACCINES The EMEA issued statements on the use of thiomersal in vaccines in 1999 and 2000 (EMEA/20962/99, EMEA/CPMP/1578/00). In light of recent reassuring data on the safety of thiomersal-containing vaccines, this new statement updates previous recommendations. Thiomersal, is an antimicrobial organic mercury compound that continues to be used either in the early stages of manufacturing, or as a preservative, in some vaccines. The antimicrobial action of thiomersal relates to ethylmercury, which is released after breakdown of thiomersal into ethylmercury and thiosalicylate. The Committee for Proprietary Medicinal Products (CPMP) previously advised that although there was no evidence of harm from thiomersal in vaccines other than hypersensitivity (allergic) reactions, it would be prudent to promote the general use of vaccines without thiomersal and other mercury containing preservatives, particularly for single dose vaccines. Since then, several vaccines licensed in the European Union have had thiomersal removed or levels reduced and new vaccines without thiomersal have been licensed. CPMP advice was in line with the global goal of reducing environmental exposure to mercury. The previous assessment of risks associated with ethylmercury had been based on data on methylmercury, as the toxicity profile of the two compounds was assumed to be similar. In March 2004, the CPMP reviewed the latest evidence relating to the safety of thiomersal-containing vaccines. -
Pyrophoric Materials
Appendix A PYROPHORIC MATERIALS Pyrophoric materials react with air, or with moisture in air. Typical reactions which occur are oxidation and hydrolysis, and the heat generated by the reactions may ignite the chemical. In some cases, these reactions liberate flammable gases which makes ignition a certainty and explosion a real possibility. Examples of pyrophoric materials are shown below. (List may not be complete) (a) Pyrophoric alkyl metals and derivatives Groups Dodecacarbonyltetracobalt Silver sulphide Dialkytzincs Dodecacarbonyltriiron Sodium disulphide Diplumbanes Hexacarbonylchromium Sodium polysulphide Trialkylaluminiums Hexacarbonylmolybdenum Sodium sulphide Trialkylbismuths Hexacarbonyltungsten Tin (II) sulphide Nonacarbonyldiiron Tin (IV) sulphide Compounds Octacarbonyldicobalt Titanium (IV) sulphide Bis-dimethylstibinyl oxide Pentacarbonyliron Uranium (IV) sulphide Bis(dimethylthallium) acetylide Tetracarbonylnickel Butyllithium (e) Pyrophoric alkyl non-metals Diethylberyllium (c) Pyrophoric metals (finely divided state) Bis-(dibutylborino) acetylene Bis-dimethylarsinyl oxide Diethylcadmium Caesium Rubidium Bis-dimethylarsinyl sulphide Diethylmagnesium Calcium Sodium Bis-trimethylsilyl oxide Diethylzinc Cerium Tantalum Dibutyl-3-methyl-3-buten-1-Yniborane Diisopropylberyllium Chromium Thorium Diethoxydimethylsilane Dimethylberyllium Cobalt Titanium Diethylmethylphosphine Dimethylbismuth chloride Hafnium Uranium Ethyldimthylphosphine Dimethylcadmium Iridium Zirconium Tetraethyldiarsine Dimethylmagnesium Iron Tetramethyldiarsine -
Mercury in Fish – Background to the Mercury in Fish Advisory Statement
Mercury in fish – Background to the mercury in fish advisory statement (March 2004) Food regulators regularly assess the potential risks associated with the presence of contaminants in the food supply to ensure that, for all sections of the population, these risks are minimised. Food Standards Australia New Zealand (FSANZ) has recently reviewed its risk assessment for mercury in food. The results from this assessment indicate that certain groups, particularly pregnant women, women intending to become pregnant and young children (up to and including 6 years), should limit their consumption of some types of fish in order to control their exposure to mercury. The risk assessment conducted by FSANZ that was published in 2004 used the most recent data and knowledge available at the time. FSANZ intends toreview the advisory statement in the future and will take any new data and scientific evidence into consideration at that time. BENEFITS OF FISH Even though certain types of fish can accumulate higher levels of mercury than others, it is widely recognised that there are considerable nutritional benefits to be derived from the regular consumption of fish. Fish is an excellent source of high biological value protein, is low in saturated fat and contains polyunsaturated fatty acids such as essential omega-3 polyunsaturates. It is also a good source of some vitamins, particularly vitamin D where a 150 g serve of fish will supply around 3 micrograms of vitamin D – about three times the amount of vitamin D in a 10 g serve of margarine. Fish forms a significant component of the Australian diet with approximately 25% of the population consuming fish at least once a week (1995 Australian National Nutrition Survey; McLennan & Podger 1999). -
Date: 1/9/2017 Question: Botulism Is an Uncommon Disorder Caused By
6728 Old McLean Village Drive, McLean, VA 22101 Tel: 571.488.6000 Fax: 703.556.8729 www.clintox.org Date: 1/9/2017 Question: Botulism is an uncommon disorder caused by toxins produced by Clostridium botulinum. Seven subtypes of botulinum toxin exist (subtypes A, B, C, D, E, F and G). Which subtypes have been noted to cause human disease and which ones have been reported to cause infant botulism specifically in the United States? Answer: According to the cited reference “Only subtypes A, B, E and F cause disease in humans, and almost all cases of infant botulism in the United States are caused by subtypes A and B. Botulinum-like toxins E and F are produced by Clostridium baratii and Clostridium butyricum and are only rarely implicated in infant botulism” (Rosow RK and Strober JB. Infant botulism: Review and clinical update. 2015 Pediatr Neurol 52: 487-492) Date: 1/10/2017 Question: A variety of clinical forms of botulism have been recognized. These include wound botulism, food borne botulism, and infant botulism. What is the most common form of botulism reported in the United States? Answer: According to the cited reference, “In the United States, infant botulism is by far the most common form [of botulism], constituting approximately 65% of reported botulism cases per year. Outside the United States, infant botulism is less common.” (Rosow RK and Strober JB. Infant botulism: Review and clinical update. 2015 Pediatr Neurol 52: 487-492) Date: 1/11/2017 Question: Which foodborne pathogen accounts for approximately 20 percent of bacterial meningitis in individuals older than 60 years of age and has been associated with unpasteurized milk and soft cheese ingestion? Answer: According to the cited reference, “Listeria monocytogenes, a gram-positive rod, is a foodborne pathogen with a tropism for the central nervous system. -
Inorganic Mercury, Methyl Mercury, Ethyl Mercury
Laboratory Procedure Manual Analyte: Inorganic mercury, Methyl mercury, Ethyl mercury Matrix: Blood Method: Blood mercury speciation TSID-GC-ICP-DRC-MS (Triple Spike Isotope Dilution Gas Chromatography- Inductively Coupled Plasma Dynamic Reaction Cell Mass Spectrometry) Method No: DLS-3020.5 Adopted: Revised: As performed by: Inorganic and Radiation Analytical Toxicology Branch Division of Laboratory Sciences National Center for Environmental Health Contact: Dr. Robert L. Jones Phone: 770-488-7991 Fax: 770-488-4097 Email: [email protected] James L. Pirkle, M.D., Ph.D. Director, Division of Laboratory Sciences Important Information for Users CDC periodically refines these laboratory methods. It is the responsibility of the user to contact the person listed on the title page of each write-up before using the analytical method to find out whether any changes have been made and what revisions, if any, have been incorporated. Mercury speciation in whole blood NHANES 2011-2012 Page 2 of 52 This document details the Lab Protocol for testing items in the following table: Data File Name Variable Name SAS Label LBXIHG Mercury, inorganic (µg/L) LBDIHGSI Mercury, inorganic (µmol/L) IHgEM_G LBXBGE Mercury, ethyl (µg/dL) LBXBGM Mercury, methyl (μg/L) Mercury speciation in whole blood NHANES 2011-2012 Page 3 of 52 1. CLINICAL RELEVANCE AND TEST PRINCIPLE A. Clinical Relevance Mercury (Hg) is widespread in the environment and found in its elemental form (Hg0), inorganic forms such as mercurous (Hg+) and mercuric (Hg2+), and various organic forms such as methyl mercury (MeHg), ethyl mercury (EtHg), phenyl mercury (PhHg), and others. The health effects of mercury are diverse and depend on the form of mercury encountered and the severity and length of 0 2+ + exposure. -
High Hazard Chemical Policy
Environmental Health & Safety Policy Manual Issue Date: 2/23/2011 Policy # EHS-200.09 High Hazard Chemical Policy 1.0 PURPOSE: To minimize hazardous exposures to high hazard chemicals which include select carcinogens, reproductive/developmental toxins, chemicals that have a high degree of toxicity. 2.0 SCOPE: The procedures provide guidance to all LSUHSC personnel who work with high hazard chemicals. 3.0 REPONSIBILITIES: 3.1 Environmental Health and Safety (EH&S) shall: • Provide technical assistance with the proper handling and safe disposal of high hazard chemicals. • Maintain a list of high hazard chemicals used at LSUHSC, see Appendix A. • Conduct exposure assessments and evaluate exposure control measures as necessary. Maintain employee exposure records. • Provide emergency response for chemical spills. 3.2 Principle Investigator (PI) /Supervisor shall: • Develop and implement a laboratory specific standard operation plan for high hazard chemical use per OSHA 29CFR 1910.1450 (e)(3)(i); Occupational Exposure to Hazardous Chemicals in Laboratories. • Notify EH&S of the addition of a high hazard chemical not previously used in the laboratory. • Ensure personnel are trained on specific chemical hazards present in the lab. • Maintain Material Safety Data Sheets (MSDS) for all chemicals, either on the computer hard drive or in hard copy. • Coordinate the provision of medical examinations, exposure monitoring and recordkeeping as required. 3.3 Employees: • Complete all necessary training before performing any work. • Observe all safety -
Methylmercury Contamination: Impacts on Aquatic Systems and Terrestrial Species, and Insights for Abatement
Methylmercury Contamination: Impacts on Aquatic Systems and Terrestrial Species, and Insights for Abatement Charles E. Sams USDA Forest Service, Eastern Region Air Quality Program, Milwaukee, Wisconsin Methylmercury (MeHg) is one of the most widespread waterborne contaminants, and through biomagnification processes has commonly been found in prey fish at concentrations toxic to piscivorous birds and mammals. In USEPA’s National Fish Tissue Survey, the Lowest Adverse Effect Concentration of 0.1 g/g wet weight was exceeded in 28% of total samples and 86% of predatory fish samples (USEPA 2002). Evidence suggests that more than a quarter of all mature fish contain methylmercury concentrations above this level. This review focuses on the leading anthropogenic sources of mercury to aquatic systems, through atmospheric deposition and the environmental dynamics of the mercury methylation process in aquatic sediments. The results of extensive mercury monitoring studies are discussed, as well as the reproductive and behavioral impacts on birds and mammals feeding on fish exhibiting realistic contaminant concentrations. Recommendations are provided for continued research and the abatement of methylmercury concentrations in fish through forest management practices. Keywords: mercury deposition, methylmercury, sulfate reducing bacteria, aquatic sediments INTRODUCTION conterminous United States, over 20.2 million ha (50 million acres) were determined to be forested wetlands, Methylmercury (MeHg) is one of the most widespread as well as 10.0 million ha (25 million acres) of emergent waterborne contaminants (USGS 2001a; UNEP 2002; wetlands and 7.3 million ha (18 million acres) of shrub USDHHS and USEPA 2004). Unhealthful levels of MeHg wetlands (Dahl 2000). While National Forest lands in fish have led to the issuance of fish consumption represent only eight percent of the contiguous United advisories by at least 46 states (USEPA 2004).