Elemental Speciation in Human Health Risk Assessment
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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. -
Tall Man Lettering List REPORT DECEMBER 2013 1
Tall Man Lettering List REPORT DECEMBER 2013 1 TALL MAN LETTERING LIST REPORT WWW.HQSC.GOVT.NZ Published in December 2013 by the Health Quality & Safety Commission. This document is available on the Health Quality & Safety Commission website, www.hqsc.govt.nz ISBN: 978-0-478-38555-7 (online) Citation: Health Quality & Safety Commission. 2013. Tall Man Lettering List Report. Wellington: Health Quality & Safety Commission. Crown copyright ©. This copyright work is licensed under the Creative Commons Attribution-No Derivative Works 3.0 New Zealand licence. In essence, you are free to copy and distribute the work (including other media and formats), as long as you attribute the work to the Health Quality & Safety Commission. The work must not be adapted and other licence terms must be abided. To view a copy of this licence, visit http://creativecommons.org/licenses/by-nd/3.0/nz/ Copyright enquiries If you are in doubt as to whether a proposed use is covered by this licence, please contact: National Medication Safety Programme Team Health Quality & Safety Commission PO Box 25496 Wellington 6146 ACKNOWLEDGEMENTS The Health Quality & Safety Commission acknowledges the following for their assistance in producing the New Zealand Tall Man lettering list: • The Australian Commission on Safety and Quality in Health Care for advice and support in allowing its original work to be either reproduced in whole or altered in part for New Zealand as per its copyright1 • The Medication Safety and Quality Program of Clinical Excellence Commission, New South -
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............................................................................................................. -
Depletion of Trace Elements and Acute Ocular Toxicity Induced by Desferrioxamine in Patients with Thalassaemia
Arch Dis Child: first published as 10.1136/adc.63.3.250 on 1 March 1988. Downloaded from Archives of Disease in Childhood, 1988, 63, 250-255 Depletion of trace elements and acute ocular toxicity induced by desferrioxamine in patients with thalassaemia S DE VIRGILIIS, M CONGIA, M P TURCO, F FRAU, C DESSI, F ARGIOLU, R SORCINELLI,* A SITZIA,* AND A CAO Istituto di Clinica e Biologia dell Eta' Evolutiva, Universita' Studi Cagliari, and *Istituto di Clinica Oculistica, Universita' Studi Cagliari, Cagliari, Sardinia, Italy SUMMARY High doses of intravenous desferrioxamine infused over a short period of time induce a large faecal and urinary iron excretion but also produce retinal abnormalities that are characterised by decreased amplitude on electroretinography and defective dark adaptation. This regimen also results in high faecal iron, zinc, and copper excretion, and reduced granulocyte zinc concentrations and alkaline phosphatase activity. The retinal abnormalities may be related to the zinc and copper deficiency and/or iron depletion 'per se' which interferes negatively with critical iron dependent enzymes. Subcutaneous infusion of desferrioxamine is the comply with the regimen of subcutaneous adminis- most efficient method for reducing the iron burden tration. in patients with thalassaemia major who are trans- fusion dependent.1 The daily infusion of 40- Patients and methods 60 mg/kg over 12 hours for six days a week is usually sufficient to obtain iron balance.'v Because some Fifteen children, aged from 9 to 16 years, with http://adc.bmj.com/ -
Chelation Therapy
Corporate Medical Policy Chelation Therapy File Name: chelation_therapy Origination: 12/1995 Last CAP Review: 2/2021 Next CAP Review: 2/2022 Last Review: 2/2021 Description of Procedure or Service Chelation therapy is an established treatment for the removal of metal toxins by converting them to a chemically inert form that can be excreted in the urine. Chelation therapy comprises intravenous or oral administration of chelating agents that remove metal ions such as lead, aluminum, mercury, arsenic, zinc, iron, copper, and calcium from the body. Specific chelating agents are used for particular heavy metal toxicities. For example, desferroxamine (not Food and Drug Administration [FDA] approved) is used for patients with iron toxicity, and calcium-ethylenediaminetetraacetic acid (EDTA) is used for patients with lead poisoning. Note that disodium-EDTA is not recommended for acute lead poisoning due to the increased risk of death from hypocalcemia. Another class of chelating agents, called metal protein attenuating compounds (MPACs), is under investigation for the treatment of Alzheimer’s disease, which is associated with the disequilibrium of cerebral metals. Unlike traditional systemic chelators that bind and remove metals from tissues systemically, MPACs have subtle effects on metal homeostasis and abnormal metal interactions. In animal models of Alzheimer’s disease, they promote the solubilization and clearance of β-amyloid protein by binding to its metal-ion complex and also inhibit redox reactions that generate neurotoxic free radicals. MPACs therefore interrupt two putative pathogenic processes of Alzheimer’s disease. However, no MPACs have received FDA approval for treating Alzheimer’s disease. Chelation therapy has also been investigated as a treatment for other indications including atherosclerosis and autism spectrum disorder. -
Cardiotoxicity of Doxorubicin Is Mediated Through Mitochondrial Iron Accumulation
Cardiotoxicity of doxorubicin is mediated through mitochondrial iron accumulation Yoshihiko Ichikawa, … , Tejaswitha Jairaj Naik, Hossein Ardehali J Clin Invest. 2014;124(2):617-630. https://doi.org/10.1172/JCI72931. Research Article Cardiology Doxorubicin is an effective anticancer drug with known cardiotoxic side effects. It has been hypothesized that doxorubicin- dependent cardiotoxicity occurs through ROS production and possibly cellular iron accumulation. Here, we found that cardiotoxicity develops through the preferential accumulation of iron inside the mitochondria following doxorubicin treatment. In isolated cardiomyocytes, doxorubicin became concentrated in the mitochondria and increased both mitochondrial iron and cellular ROS levels. Overexpression of ABCB8, a mitochondrial protein that facilitates iron export, in vitro and in the hearts of transgenic mice decreased mitochondrial iron and cellular ROS and protected against doxorubicin-induced cardiomyopathy. Dexrazoxane, a drug that attenuates doxorubicin-induced cardiotoxicity, decreased mitochondrial iron levels and reversed doxorubicin-induced cardiac damage. Finally, hearts from patients with doxorubicin-induced cardiomyopathy had markedly higher mitochondrial iron levels than hearts from patients with other types of cardiomyopathies or normal cardiac function. These results suggest that the cardiotoxic effects of doxorubicin develop from mitochondrial iron accumulation and that reducing mitochondrial iron levels protects against doxorubicin- induced cardiomyopathy. Find the latest version: https://jci.me/72931/pdf Research article Cardiotoxicity of doxorubicin is mediated through mitochondrial iron accumulation Yoshihiko Ichikawa,1 Mohsen Ghanefar,1 Marina Bayeva,1 Rongxue Wu,1 Arineh Khechaduri,1 Sathyamangla V. Naga Prasad,2 R. Kannan Mutharasan,1 Tejaswitha Jairaj Naik,1 and Hossein Ardehali1 1Feinberg Cardiovascular Institute, Northwestern University School of Medicine, Chicago, Illinois, USA. -
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 -
PROVISIONAL PEER REVIEWED TOXICITY VALUES for DIMETHYLMERCURY (CASRN 593-74-8) Derivation of Subchronic and Chronic Oral Rfds
EPA/690/R-04/005F l Final 12-01-2004 Provisional Peer Reviewed Toxicity Values for Dimethylmercury (CASRN 593-74-8) Derivation of Subchronic and Chronic Oral RfDs Superfund Health Risk Technical Support Center National Center for Environmental Assessment Office of Research and Development U.S. Environmental Protection Agency Cincinnati, OH 45268 Acronyms and Abbreviations bw body weight cc cubic centimeters CD Caesarean Delivered CERCLA Comprehensive Environmental Response, Compensation and Liability Act of 1980 CNS central nervous system cu.m cubic meter DWEL Drinking Water Equivalent Level FEL frank-effect level FIFRA Federal Insecticide, Fungicide, and Rodenticide Act g grams GI gastrointestinal HEC human equivalent concentration Hgb hemoglobin i.m. intramuscular i.p. intraperitoneal i.v. intravenous IRIS Integrated Risk Information System IUR inhalation unit risk kg kilogram L liter LEL lowest-effect level LOAEL lowest-observed-adverse-effect level LOAEL(ADJ) LOAEL adjusted to continuous exposure duration LOAEL(HEC) LOAEL adjusted for dosimetric differences across species to a human m meter MCL maximum contaminant level MCLG maximum contaminant level goal MF modifying factor mg milligram mg/kg milligrams per kilogram mg/L milligrams per liter MRL minimal risk level i MTD maximum tolerated dose MTL median threshold limit NAAQS National Ambient Air Quality Standards NOAEL no-observed-adverse-effect level NOAEL(ADJ) NOAEL adjusted to continuous exposure duration NOAEL(HEC) NOAEL adjusted for dosimetric differences across species to a -
Speciation of Volatile Arsenic at Geothermal Features in Yellowstone National Park
Geochimica et Cosmochimica Acta 70 (2006) 2480–2491 www.elsevier.com/locate/gca Speciation of volatile arsenic at geothermal features in Yellowstone National Park Britta Planer-Friedrich a,*, Corinne Lehr b,c,Jo¨rg Matschullat d, Broder J. Merkel a, Darrell Kirk Nordstrom e, Mark W. Sandstrom f a Technische Universita¨t Bergakademie Freiberg, Department of Geology, 09599 Freiberg, Germany b Montana State University, Thermal Biology Institute Bozeman, MT 59717, USA c California Polytechnic State University, Department of Chemistry and Biochemistry, San Luis Obispo, CA 93407, USA d Technische Universita¨t Bergakademie Freiberg, Department of Mineralogy, 09599 Freiberg, Germany e US Geological Survey, 3215 Marine St, Boulder, CO 80303, USA f US Geological Survey, National Water Quality Laboratory, Denver, CO 80225-004, USA Received 2 September 2005; accepted in revised form 7 February 2006 Abstract Geothermal features in the Yellowstone National Park contain up to several milligram per liter of aqueous arsenic. Part of this arsenic is volatilized and released into the atmosphere. Total volatile arsenic concentrations of 0.5–200 mg/m3 at the surface of the hot springs were found to exceed the previously assumed nanogram per cubic meter range of background concentrations by orders of magnitude. Speciation of the volatile arsenic was performed using solid-phase micro-extraction fibers with analysis by GC–MS. The arsenic species most frequently identified in the samples is (CH3)2AsCl, followed by (CH3)3As, (CH3)2AsSCH3, and CH3AsCl2 in decreasing order of frequency. This report contains the first documented occurrence of chloro- and thioarsines in a natural environment. Toxicity, mobility, and degradation products are unknown.