University of Cincinnati

Total Page:16

File Type:pdf, Size:1020Kb

University of Cincinnati UNIVERSITY OF CINCINNATI Date:___________________ I, _________________________________________________________, hereby submit this work as part of the requirements for the degree of: in: It is entitled: This work and its defense approved by: Chair: _______________________________ _______________________________ _______________________________ _______________________________ _______________________________ Comparison Study Between OSHA Rule of Thumb and Software Model Respirator Cartridge Service Life Thesis submitted to the University of Cincinnati Division of Graduate Studies in partial fulfillment of the requirements for the degree of Master of Science In the Department of Environmental Health of the College of Medicine 8-12-2008 by Celeste Hemphill B.S., Eastern Kentucky University, 2005 Committee: Roy McKay, Ph.D. (Chair) Glenn Talaska, Ph.D. Paul Succop, Ph.D. Abstract This study was conducted to determine the percentage of time the OSHA Rule of Thumb for respirator cartridge service life agrees with a computer calculated model for CBRN-approved air purifying respirators. Test conditions used and organic vapors evaluated in the OSHA/NIOSH MultiVapor software model were chosen from the NIOSH certification testing criteria for CBRN respirators. Service life predicted from the software model evaluated at concentrations of 2600, 260, 26, and 2.6 ppm was compared to the OSHA Rule of Thumb. When determining service life for CBRN approved respirators, applying the OSHA Rule of Thumb was found to be most successful at 26 ppm (96.6%). Success rate of the OSHA Rule of Thumb was found to be 93.2% and 94.9% at the concentrations of 260 and 2.6 ppm, respectively. Statistical analysis of the data indicates the OSHA Rule of Thumb to be acceptable in determining service life for CBRN approved respirators. ii iii Acknowledgements I would like to give my deepest thanks to my advisor Dr. Roy McKay for encouragement and guidance through this project. I would also like to thank my thesis committee members, Dr. Glenn Talaska and Dr. Paul Succop of the University of Cincinnati for their guidance and assistance with this project. This research was partially by the National Institute for Occupational Health (NIOSH) University of Cincinnati Education and Research Center Grant #T42- OH008432-03 and the Powell/Cohrssen Scholarship fund. Without the assistance of this I would not have been able to gain valuable experience at the University of Cincinnati and conduct this research project. Lastly I would like to thank my family and friends that supported me as I have worked my way through school. iv Table of Contents Abstract…………………………………………………………………………....ii Acknowledgements……………………………………………………………….iv Table of Contents………………………………………………………………….v List of Tables……………………………………………………………………..vi List of Figures……………………………………………………………………vii I. Introduction………………………………………………………………..8 II. Methods…………………………………………………………………..13 III. Results……………………………………………………………………15 IV. Conclusions………………………………………………………………22 V. Tables…………………………………………………………………….27 VI. Figures…………………………………………………………………....43 VII. References………………………………………………………………..46 VIII. Appendices……………………………………………………………….48 v List of Tables 1. TIC/TIM Families and TRA…………………………………………………27 2. Canister Test Challenge and Breakthrough Concentrations…………………28 3. Organic Vapors Evaluated in This Study and Corresponding CAS #.............29 4. NIOSH Certification Testing Conditions…………………………………….31 5. Software Model Cartridge Data……………………………………………...32 6. Exposure Limits……………………………………………………………...33 7. OSHA Rule of Thumb……………………………………………………….34 8. OSHA Rule of Thumb Applicability at 25% Relative Humidity……………35 9. OSHA Rule of Thumb Applicability at 80% Relative Humidity……………36 10. OSHA Rule of Thumb Applicability at Both Relative Humidity’s………….37 11. Summary of OSHA Rule of Thumb Applicability…………………………..38 12. χ2 for OSHA Rule of Thumb at 25% Relative Humidity…………………...39 13. χ2 for OSHA Rule of Thumb at 80% Relative Humidity…………………...40 14. χ2 for OSHA Rule of Thumb at Both Relative Humidity’s Combined…….41 15. Chi Square ( χ2 ) Distribution Table………………………………………….42 vi List of Figures 1. OSHA Rule of Thumb Applicability at 25% Relative Humidity……………43 2. OSHA Rule of Thumb Applicability at 80% Relative Humidity……………44 3. OSHA Rule of Thumb Applicability Comparison at 25% and 80% Relative Humidity……………………………………………………………45 vii I. Introduction The first lines of defense to protect workers from harmful chemical and physical agents encountered in the workplace are engineering and administrative controls. When engineering and administrative controls are found to not protect the worker, personal protective equipment is used. Use of personal protective equipment in the workplace is regulated by the Occupational Safety and Health Administration (OSHA). Employers are required to provide an employee a respirator that protects from exposure to harmful airborne contaminants. OSHA’s Respiratory Protection Standard, 29 CFR 1910.134 states that when respirators are used in the workplace, a written respiratory protection program must be established and implemented by the employer. This program must include procedures for the following: respirator selection, medical evaluations of employees required to wear respirators, fit testing for tight-fitting respirators, proper use of respirators in routine and emergency situations, schedules for respirator maintenance; adequate air quality, quantity, flow of breathing air for atmosphere supplying respirators, training of employees of the respiratory hazards of potential exposure, training of employees in the proper use of respirators, and evaluation for the effectiveness of the program. Once a respirator has been selected, a requirement in the respiratory protection program is the development and implementation of a cartridge change-out schedule for the conditions in which the chosen respirator will be used (OSHA, 2006). 8 A respirator cartridge change-out schedule is used to determine the length of time that a cartridge can be used before being discarded and replaced. Service life is the length of time a cartridge will effectively remove contaminants from the incoming air stream. Calculating the breakthrough time that a contaminant can be detected on the downside of the cartridge is one method that can be used to determine cartridge service life (Plog, 2002). Other methods include: experimental testing, math models, or manufacturer’s recommendations (OSHA, 2006). When using these methods, several factors must be considered to calculate the cartridge service life including: cartridge type, concentration of the contaminant, temperature, humidity, filtering capacity of cartridge, pattern of respirator use, and breathing rate (Plog, 2002). Once all factors have been considered and the service life of the cartridges determined, a change-out schedule can be developed and implemented in a written respiratory protection program. An accurate cartridge change-out schedule must be implemented to ensure that workers are adequately protected from exposure to harmful airborne contaminants in the workplace. A quick method used to determine the service life of a cartridge is the Rule of Thumb developed by OSHA. This method can be applied to determine the cartridge service life when exposed to chemicals at varying environmental conditions. The Rule of Thumb consists of four suggestions: (1) if a chemical’s boiling point is above 70ºC and the contaminant concentration is less than 200 parts per million (ppm), service life is generally expected to be 8 hours at a normal work rate; (2) cartridge service life 9 is inversely proportional to work rate; (3) when the concentration is decreased by a factor of 10, the service life is increased by a factor of 5; (4) service life is reduced by 50% when the relative humidity is above 85% (OSHA, 2007). This study will be conducted with the suggestion concerning the concentration. For example, if the service life of a cartridge at 100 ppm is 30 minutes; when the concentration is reduced 10 fold to 10 ppm, the service life can be increased to 150 minutes. The generalizations of the Rule of Thumb are thought to be correct, but service life should be determined in conjunction with other methods such as math models or software programs. OSHA and NIOSH have developed the software program MultiVapor, which is used to determine the cartridge service life. This program allows the user to enter in parameters of the cartridge being evaluated, the environmental conditions in which the cartridge will be used, the contaminant(s) the cartridge will be used against, and the contaminant airborne and breakthrough concentrations. Once all parameters have been entered into the program, an estimated average breakthrough time will be given, along with the minimum and maximum breakthrough time in minutes. When choosing a respirator, the employer must select and provide one appropriate to protect the worker from the respiratory hazards that are potentially present in the workplace. OSHA’s Respiratory Protection Standard requires all respirators to be certified by The National Institute for Occupational Safety and Health (NIOSH) and used in compliance with the respirator’s certification (OSHA, 2006). Within The Centers for Disease Control and Prevention (CDC) and in the Department of Health and Human Services (DHHS), NIOSH is the regulatory agency responsible for testing 10 and certifying respirators and cartridges as well as issuing recommendations for the use of respirators (NIOSH,
Recommended publications
  • Regulated Substance List
    INSTRUCTIONS FOR THE UNIFIED PROGRAM (UP) FORM REGULATED SUBSTANCE LIST CHEMICAL NAME CAS # TQ Listing CHEMICAL NAME CAS # TQ Listing (Lbs) Basis (Lbs) Basis Acetaldehyde 75-07-0 10,000 g Cantharidin 56-25-7 100/10,0001 * Acetone Cyanohydrin 75-86-5 1,000 Carbachol Chloride 51-83-2 500/10,0001 Acetone Thiosemicarbazide 1752-30-3 1,000/10,0001 Acetylene (Ethyne) 74-86-2 10,000 f Carbamic Acid, Methyl-,o- Acrolein (2-Propenal) 107-02-8 500 b (((2,4-Dimethyl-1,3-Dithiolan- Acrylamide 79-06-1 1,000/10,0001 2-YL) Methylene)Amino)- 26419-73-8 100/10,0001 Acrylonitrile (2- Propenenitrile) 107-13-1 10,000 b Carbofuran 1563-66-2 10/10,0001 Acrylyl Chloride Carbon Disulfide 75-15-0 10,000 b (2-Propenoyl Chloride) 814-68-6 100 b Carbon Oxysulfide Aldicarb 116-06-3 100/10,0001 (Carbon Oxide Sulfide (COS)) 463-58-1 10,000 f Aldrin 309-00-2 500/10,0001 Chlorine 7782-50-5 100 a,b Allyl Alcohol (2-Propen-1-ol) 107-18-6 1,000 b Chlorine Dioxide Allylamine (2-Propen-1-Amine) 107-11-9 500 b (Chlorine Oxide (ClO2)) 10049-04-4 1,000 c Aluminum Phosphide 20859-73-8 500 Chlorine Monoxide (Chlorine Oxide) 7791-21-1 10,000 f Aminopterin 54-62-6 500/10,0001 Chlormequat Chloride 999-81-5 100/10,0001 Amiton Oxalate 3734-97-2 100/10,0001 Chloroacetic Acid 79-11-8 100/10,0001 Ammonia, Anhydrous 2 7664-41-7 500 a,b Chloroform 67-66-3 10,000 b Ammonia, Aqueous Chloromethyl Ether (conc 20% or greater) 7664-41-7 20,000 a,b (Methane,Oxybis(chloro-) 542-88-1 100 b * Aniline 62-53-3 1,000 Chloromethyl Methyl Ether Antimycin A 1397-94-0 1,000/10,0001 (Chloromethoxymethane)
    [Show full text]
  • COMBINED LIST of Particularly Hazardous Substances
    COMBINED LIST of Particularly Hazardous Substances revised 2/4/2021 IARC list 1 are Carcinogenic to humans list compiled by Hector Acuna, UCSB IARC list Group 2A Probably carcinogenic to humans IARC list Group 2B Possibly carcinogenic to humans If any of the chemicals listed below are used in your research then complete a Standard Operating Procedure (SOP) for the product as described in the Chemical Hygiene Plan. Prop 65 known to cause cancer or reproductive toxicity Material(s) not on the list does not preclude one from completing an SOP. Other extremely toxic chemicals KNOWN Carcinogens from National Toxicology Program (NTP) or other high hazards will require the development of an SOP. Red= added in 2020 or status change Reasonably Anticipated NTP EPA Haz list COMBINED LIST of Particularly Hazardous Substances CAS Source from where the material is listed. 6,9-Methano-2,4,3-benzodioxathiepin, 6,7,8,9,10,10- hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide Acutely Toxic Methanimidamide, N,N-dimethyl-N'-[2-methyl-4-[[(methylamino)carbonyl]oxy]phenyl]- Acutely Toxic 1-(2-Chloroethyl)-3-(4-methylcyclohexyl)-1-nitrosourea (Methyl-CCNU) Prop 65 KNOWN Carcinogens NTP 1-(2-Chloroethyl)-3-cyclohexyl-1-nitrosourea (CCNU) IARC list Group 2A Reasonably Anticipated NTP 1-(2-Chloroethyl)-3-cyclohexyl-1-nitrosourea (CCNU) (Lomustine) Prop 65 1-(o-Chlorophenyl)thiourea Acutely Toxic 1,1,1,2-Tetrachloroethane IARC list Group 2B 1,1,2,2-Tetrachloroethane Prop 65 IARC list Group 2B 1,1-Dichloro-2,2-bis(p -chloropheny)ethylene (DDE) Prop 65 1,1-Dichloroethane
    [Show full text]
  • Downloads/DL Praevention/Fachwissen/Gefahrstoffe/TOXIKOLOGI SCHE BEWERTUNGEN/Bewertungen/Toxbew072-L.Pdf
    Distribution Agreement In presenting this thesis or dissertation as a partial fulfillment of the requirements for an advanced degree from Emory University, I hereby grant to Emory University and its agents the non-exclusive license to archive, make accessible, and display my thesis or dissertation in whole or in part in all forms of media, now or hereafter known, including display on the world wide web. I understand that I may select some access restrictions as part of the online submission of this thesis or dissertation. I retain all ownership rights to the copyright of the thesis or dissertation. I also retain the right to use in future works (such as articles or books) all or part of this thesis or dissertation. Signature: _____________________________ ______________ Jedidiah Samuel Snyder Date Statistical analysis of concentration-time extrapolation factors for acute inhalation exposures to hazardous substances By Jedidiah S. Snyder Master of Public Health Global Environmental Health _________________________________________ P. Barry Ryan, Ph.D. Committee Chair _________________________________________ Eugene Demchuk, Ph.D. Committee Member _________________________________________ Paige Tolbert, Ph.D. Committee Member Statistical analysis of concentration-time extrapolation factors for acute inhalation exposures to hazardous substances By Jedidiah S. Snyder Bachelor of Science in Engineering, B.S.E. The University of Iowa 2010 Thesis Committee Chair: P. Barry Ryan, Ph.D. An abstract of A thesis submitted to the Faculty of the Rollins School of Public Health of Emory University in partial fulfillment of the requirements for the degree of Master of Public Health in Global Environmental Health 2015 Abstract Statistical analysis of concentration-time extrapolation factors for acute inhalation exposures to hazardous substances By Jedidiah S.
    [Show full text]
  • Warfare Agents for Modeling Airborne Dispersion in and Around Buildings
    LBNL-45475 ERNEST ORLANDO LAWRENCE BERKELEY NATIn NAL LABORATORY Databaseof Physical,Chemicaland ToxicologicalPropertiesof Chemical and Biological(CB)WarfitreAgentsfor ModelingAirborneDispersionIn and AroundBuildings TracyThatcher,RichSextro,andDonErmak Environmental Energy Technologies Division DISCLAIMER This document was prepared as an account of work sponsored by the United States Government. While this document is believed to contain correct information, neither the United States Government nor any agency thereof, nor The Regents of the University of Catifomia, nor any of their employees, makes any warranty, express or implied, or assumes any legal responsibility for the accuracy, completeness, or usefulness of anY information, apparatus, product, or process disclosed, or represents that its use would not infringe privately owned rights. Reference herein to any specific commercial product, process, or service by its trade name, trademark, manufacturer, or otherwise, does not necessarily constitute or imply its endorsement, recommend at i on, or favoring by the United States Government or any agency thereof, or The Regents of the University of California. The views and opinions of authors expressed herein do not necessarily state or reflect those of the United States Government or any agency thereof, or The Regents of the University of California. Ernest Orlando Lawrence Berkeley National Laboratory is an equal opportunity employer. DISCLAIMER Portions of this document may be illegible in electronic image products. Images are produced
    [Show full text]
  • Five Tyrosines and Two Serines in Human Albumin Are Labeled by the Organophosphorus Agent FP-Biotin
    View metadata, citation and similar papers at core.ac.uk brought to you by CORE Chem. Res. Toxicol. 2008, 21, 1787–1794 1787 provided by PubMed Central Five Tyrosines and Two Serines in Human Albumin Are Labeled by the Organophosphorus Agent FP-Biotin Shi-Jian Ding,† John Carr,† James E. Carlson,‡ Larry Tong,§ Weihua Xue,§ Yifeng Li,† Lawrence M. Schopfer,§ Bin Li,§ Florian Nachon,| Oluwatoyin Asojo,† Charles M. Thompson,⊥ Steven H. Hinrichs,† Patrick Masson,| and Oksana Lockridge*,§ Department of Pathology and Microbiology, UniVersity of Nebraska Medical Center, Omaha, Nebraska 68198, Applied Biosystems, Framingham, Massachusetts 01701, Eppley Institute, UniVersity of Nebraska Medical Center, Omaha, Nebraska 68198, Centre de Recherches d SerVice de Sante´ des Arme´es, Unite´ d’Enzymologie, BP87, 38702 La Tronche Cedex, France, and Department of Biomedical and Pharmaceutical Sciences, UniVersity of Montana, Missoula, Montana 59812 ReceiVed April 23, 2008 Tyrosine 411 of human albumin is an established site for covalent attachment of 10-fluoroethoxyphosphinyl- N-biotinamidopentyldecanamide (FP-biotin), diisopropylfluorophosphate, chlorpyrifos oxon, soman, sarin, and dichlorvos. This work investigated the hypothesis that other residues in albumin could be modified by organophosphorus agents (OP). Human plasma was aggressively treated with FP-biotin; plasma proteins were separated into high and low abundant portions using a proteome partitioning antibody kit, and the proteins were digested with trypsin. The FP-biotinylated tryptic peptides were isolated by binding to monomeric avidin beads. The major sites of covalent attachment identified by mass spectrometry were Y138, Y148, Y401, Y411, Y452, S232, and S287 of human albumin. Prolonged treatment of pure human albumin with chlorpyrifos oxon labeled Y138, Y150, Y161, Y401, Y411, and Y452.
    [Show full text]
  • SAPRC07T Mechanism Species Definition Molecular Weight ACETONE Acetone 58.08 ACETYLENE Acetylene 26.04 ACROLEIN Acrolein 56.06 A
    SAPRC07T Mechanism Species Molecular Species Definition weight ACETONE Acetone 58.08 ACETYLENE Acetylene 26.04 ACROLEIN Acrolein 56.06 ACROLEIN_PRIMARY Acrolein emissions tracer 56.06 Lumped photoreactive monounsaturated dicarbonyl aromatic AFG1 fragmentation products that photolyze to form radicals 98.10 Lumped photoreactive monounsaturated dicarbonyl aromatic fragmentation products that photolyze to form non-radical AFG2 products 98.10 Lumped diunsaturatred dicarbonyl aromatic fragmentation AFG3 product. 124.14 Alkanes and other non-aromatic compounds that react only with OH, and have kOH between 2 and 5 x 102 ppm-1 min-1. ALK1 (Primarily ethane) 30.07 Alkanes and other non-aromatic compounds that react only with OH, and have kOH between 5 x 102 and 2.5 x 103 ppm-1 ALK2 min-1. (Primarily propane and acetylene) 36.73 Alkanes and other non-aromatic compounds that react only with OH, and have kOH between 2.5 x 103 and 5 x 103 ppm-1 ALK3 min-1. 58.61 Alkanes and other non-aromatic compounds that react only with OH, and have kOH between 5 x 103 and 1 x 104 ppm-1 ALK4 min-1. 77.6 Alkanes and other non-aromatic compounds that react only ALK5 with OH, and have kOH greater than 1 x 104 ppm-1 min-1. 118.89 SAPRC07T Mechanism Species Molecular Species Definition weight SOA precursor compounds products from largest alkanes ALK5RXN (ALK5) 118.9 APIN -pinene 136.23 ARO1 Aromatics with kOH < 2x104 ppm-1 min-1. 95.16 ARO2 Aromatics with kOH > 2x104 ppm-1 min-1. 118.72 BACL Biacetyl 86.09 BALD Aromatic aldehydes (e.g., benzaldehyde) 106.13 BENZENE Benzene 78.11 SOA precursor compounds from benzene via peroxy radical BNZHRXN reaction with HO2 127 SOA precursor compounds from benzene via peroxy radical BNZNRXN reaction with NO 127 BNZRO2 SOA precursor surrogate from benzene 127 BUTADIENE13 1,3-butadiene 54.09 BZCO3 Peroxyacyl radical formed from Aromatic Aldehydes 137.11 BZO Phenoxy Radicals 93 CCHO Acetaldehyde 44.05 CCHO_PRIMARY Acetaldehyde Emissions Tracer 44.05 CCOOH Acetic Acid.
    [Show full text]
  • Kinetic Modeling of the Thermal Destruction of Nitrogen Mustard
    Kinetic Modeling of the Thermal Destruction of Nitrogen Mustard Gas Juan-Carlos Lizardo-Huerta, Baptiste Sirjean, Laurent Verdier, René Fournet, Pierre-Alexandre Glaude To cite this version: Juan-Carlos Lizardo-Huerta, Baptiste Sirjean, Laurent Verdier, René Fournet, Pierre-Alexandre Glaude. Kinetic Modeling of the Thermal Destruction of Nitrogen Mustard Gas. Journal of Physical Chemistry A, American Chemical Society, 2017, 121 (17), pp.3254-3262. 10.1021/acs.jpca.7b01238. hal-01708219 HAL Id: hal-01708219 https://hal.archives-ouvertes.fr/hal-01708219 Submitted on 13 Feb 2018 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Kinetic Modeling of the Thermal Destruction of Nitrogen Mustard Gas Juan-Carlos Lizardo-Huerta†, Baptiste Sirjean†, Laurent Verdier‡, René Fournet†, Pierre-Alexandre Glaude†,* †Laboratoire Réactions et Génie des Procédés, CNRS, Université de Lorraine, 1 rue Grandville BP 20451 54001 Nancy Cedex, France ‡DGA Maîtrise NRBC, Site du Bouchet, 5 rue Lavoisier, BP n°3, 91710 Vert le Petit, France *corresponding author: [email protected] Abstract The destruction of stockpiles or unexploded ammunitions of nitrogen mustard (tris (2- chloroethyl) amine, HN-3) requires the development of safe processes.
    [Show full text]
  • Nerve Agent - Lntellipedia Page 1 Of9 Doc ID : 6637155 (U) Nerve Agent
    This document is made available through the declassification efforts and research of John Greenewald, Jr., creator of: The Black Vault The Black Vault is the largest online Freedom of Information Act (FOIA) document clearinghouse in the world. The research efforts here are responsible for the declassification of MILLIONS of pages released by the U.S. Government & Military. Discover the Truth at: http://www.theblackvault.com Nerve Agent - lntellipedia Page 1 of9 Doc ID : 6637155 (U) Nerve Agent UNCLASSIFIED From lntellipedia Nerve Agents (also known as nerve gases, though these chemicals are liquid at room temperature) are a class of phosphorus-containing organic chemicals (organophosphates) that disrupt the mechanism by which nerves transfer messages to organs. The disruption is caused by blocking acetylcholinesterase, an enzyme that normally relaxes the activity of acetylcholine, a neurotransmitter. ...--------- --- -·---- - --- -·-- --- --- Contents • 1 Overview • 2 Biological Effects • 2.1 Mechanism of Action • 2.2 Antidotes • 3 Classes • 3.1 G-Series • 3.2 V-Series • 3.3 Novichok Agents • 3.4 Insecticides • 4 History • 4.1 The Discovery ofNerve Agents • 4.2 The Nazi Mass Production ofTabun • 4.3 Nerve Agents in Nazi Germany • 4.4 The Secret Gets Out • 4.5 Since World War II • 4.6 Ocean Disposal of Chemical Weapons • 5 Popular Culture • 6 References and External Links --------------- ----·-- - Overview As chemical weapons, they are classified as weapons of mass destruction by the United Nations according to UN Resolution 687, and their production and stockpiling was outlawed by the Chemical Weapons Convention of 1993; the Chemical Weapons Convention officially took effect on April 291997. Poisoning by a nerve agent leads to contraction of pupils, profuse salivation, convulsions, involuntary urination and defecation, and eventual death by asphyxiation as control is lost over respiratory muscles.
    [Show full text]
  • Aegls Brochure
    4.85 5 5 About the Board on Environmental Studies and Toxicology The Board on Environmental Studies and Toxicology addresses Types of Chemicals Covered in the AEGLs Series environmental pollution problems affecting human health, human impacts on the environment, and the assessment and management of risks to AEGLs values for the chemicals listed below were published in the first human health and the environment. The board’s reports answer questions six volumes of the AEGLs series. AEGLs for additional chemicals will about air and water pollution; solid and hazardous waste; toxicology; continue to be published in subsequent volumes. epidemiology; risk assessment; applied ecology; natural resources; and environmental engineering, economics, law, and policy. Allylamine Hydrogen fluoride Ammonia Iron pentacarbonyl Aniline Methyl hydrazine Arsine Methyl isocyanate About NRC Reports from the National Academies Protecting Chlorine Nerve agents GA [tabun], The National Academies, through its National Research Council reports, Chlorine dioxide GB [sarin], GD [soman], GF, provides a unique public service by working outside the framework of Chlorine trifluoride and VX the Public and government to ensure independent, expert advice on matters of science, Crotonaldehyde Nickel carbonyl technology, and medicine. Today, the National Academies include three Cyclohexylamine Phosgene honorary societies that elect new members to their ranks each year- Diborane Phosphine Emergency the National Academy of Sciences, the National Academy of Engineering, 1,1-Dichloro-1-fluoroethane Propylene glycol dinitrate and the Institute of Medicine-and the National Research Council, the (HCFC-141B) Sulfur mustard operating arm that conducts the bulk of the institution’s Dimethylhydrazine 1,1,1,2-Tetrafluoroethane Workers science-policy and technical work.
    [Show full text]
  • Argonne Report.Pdf
    CONTENTS NOTATION ........................................................................................................................... xi ABSTRACT ........................................................................................................................... 1 1 INTRODUCTION ........................................................................................................... 5 1.1 Overview of the Emergency Response Guidebook ................................................ 5 1.2 Organization of this Report ..................................................................................... 7 2 GENERAL METHODOLOGY ....................................................................................... 9 2.1 TIH List ................................................................................................................... 10 2.1.1 Background ................................................................................................. 10 2.1.2 Changes in the TIH List for the ERG2012 ................................................. 11 2.2 Shipment and Release Scenarios ............................................................................ 11 2.2.1 Shipment Profiles ........................................................................................ 12 2.2.2 Treatment of Chemical Agents ................................................................... 14 2.3 Generics, Mixtures, and Solutions .......................................................................... 17 2.4 Analysis of Water-Reactive
    [Show full text]
  • Chemical Name Federal P Code CAS Registry Number Acutely
    Acutely / Extremely Hazardous Waste List Federal P CAS Registry Acutely / Extremely Chemical Name Code Number Hazardous 4,7-Methano-1H-indene, 1,4,5,6,7,8,8-heptachloro-3a,4,7,7a-tetrahydro- P059 76-44-8 Acutely Hazardous 6,9-Methano-2,4,3-benzodioxathiepin, 6,7,8,9,10,10- hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide P050 115-29-7 Acutely Hazardous Methanimidamide, N,N-dimethyl-N'-[2-methyl-4-[[(methylamino)carbonyl]oxy]phenyl]- P197 17702-57-7 Acutely Hazardous 1-(o-Chlorophenyl)thiourea P026 5344-82-1 Acutely Hazardous 1-(o-Chlorophenyl)thiourea 5344-82-1 Extremely Hazardous 1,1,1-Trichloro-2, -bis(p-methoxyphenyl)ethane Extremely Hazardous 1,1a,2,2,3,3a,4,5,5,5a,5b,6-Dodecachlorooctahydro-1,3,4-metheno-1H-cyclobuta (cd) pentalene, Dechlorane Extremely Hazardous 1,1a,3,3a,4,5,5,5a,5b,6-Decachloro--octahydro-1,2,4-metheno-2H-cyclobuta (cd) pentalen-2- one, chlorecone Extremely Hazardous 1,1-Dimethylhydrazine 57-14-7 Extremely Hazardous 1,2,3,4,10,10-Hexachloro-6,7-epoxy-1,4,4,4a,5,6,7,8,8a-octahydro-1,4-endo-endo-5,8- dimethanonaph-thalene Extremely Hazardous 1,2,3-Propanetriol, trinitrate P081 55-63-0 Acutely Hazardous 1,2,3-Propanetriol, trinitrate 55-63-0 Extremely Hazardous 1,2,4,5,6,7,8,8-Octachloro-4,7-methano-3a,4,7,7a-tetra- hydro- indane Extremely Hazardous 1,2-Benzenediol, 4-[1-hydroxy-2-(methylamino)ethyl]- 51-43-4 Extremely Hazardous 1,2-Benzenediol, 4-[1-hydroxy-2-(methylamino)ethyl]-, P042 51-43-4 Acutely Hazardous 1,2-Dibromo-3-chloropropane 96-12-8 Extremely Hazardous 1,2-Propylenimine P067 75-55-8 Acutely Hazardous 1,2-Propylenimine 75-55-8 Extremely Hazardous 1,3,4,5,6,7,8,8-Octachloro-1,3,3a,4,7,7a-hexahydro-4,7-methanoisobenzofuran Extremely Hazardous 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O- [(methylamino)-carbonyl]oxime 26419-73-8 Extremely Hazardous 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O- [(methylamino)-carbonyl]oxime.
    [Show full text]
  • Measurement Technique for the Determination of Photolyzable
    JOURNAL OF GEOPHYSICAL RESEARCH, VOL. 102, NO. D13, PAGES 15,999-16,004,JULY 20, 1997 Measurement techniquefor the determination of photolyzable chlorine and bromine in the atmosphere G. A. Impey,P. B. Shepson,• D. R. Hastie,L. A. Bartie• Departmentof Chemistryand Centre for AtmosphericChemistry, York University,Toronto, Ontario, Canada Abstract. A techniquehas been developed to enablemeasurement of photolyzablechlorine and bromineat tracelevels in the troposphere.In thismethod, ambient air is drawnt•ough a cylindricalflow cell, whichis irradiatedwith a Xe arc lamp. In the reactionvessel of the photoactivehalogen detector (PHD), photolyrically active molecules Clp (including C12, HOC1, C1NO,C1NO2, and C1ONO2) and Brp (including Br2, HOBr, BrNO, BrNO2, and BrONO2) are photolyzed,and the halogenatoms produced react with properieto form stablehalogenated products.These products are thensampled and subsequently separated and detected by gas chromatography.The systemis calibratedusing low concentrationmixtures of C12and Br2 in air from commerciallyavailable permeation sources. We obtaineddetection limits of 4 pptv and 9 pptv as Br2 andC12, respectively, for 36 L samples. 1. Introduction (or C12)in the Arctic, largely as a result of the lack of suitable analyticalmethodologies. This paperreports the developmentof The episodicdestruction of groundlevel ozonein the Arctic at a measurementtechnique for the determinationof rapidly sunriseis a phenomenonthat hasbeen observed for many years. photolyzingchlorine (referred to hereas Clp) and bromine (Brp) With the onsetof polar sunrise,ozone levels are often observed speciesat pansper trillion by volume(pptv) mixingratios in the to drop from a backgroundconcentration of •40 ppbv to almost atmosphere.Impey et al. [this issue]discuss the resultsobserved zero on a timescaleof a day or less [Barrie et al., 1988] for from a field studyconducted in the Canadianhigh Arctic at Alert, periodsof 1-10 days.
    [Show full text]