Epa Hazardous Waste Codes

Total Page:16

File Type:pdf, Size:1020Kb

Epa Hazardous Waste Codes EPA HAZARDOUS WASTE CODES Code Waste description Code Waste description D001 Ignitable waste D023 o-Cresol D002 Corrosive waste D024 m-Cresol D003 Reactive waste D025 p-Cresol D004 Arsenic D026 Cresol D005 Barium D027 1,4-Dichlorobenzene D006 Cadmium D028 1,2-Dichloroethane D007 Chromium D029 1,1-Dichloroethylene D008 Lead D030 2,4-Dinitrotoluene D009 Mercury D031 Heptachlor (and its epoxide) D010 Selenium D032 Hexachlorobenzene D011 Silver D033 Hexachlorobutadiene D012 Endrin(1,2,3,4,10,10-hexachloro-1,7-epoxy- D034 Hexachloroethane 1,4,4a,5,6,7,8,8a-octahydro-1,4-endo, endo- 5,8-dimeth-ano-naphthalene) D035 Methyl ethyl ketone D013 Lindane (1,2,3,4,5,6-hexa- D036 Nitrobenzene chlorocyclohexane, gamma isomer) D037 Pentachlorophenol D014 Methoxychlor (1,1,1-trichloro-2,2-bis [p- methoxyphenyl] ethane) D038 Pyridine D015 Toxaphene (C10 H10 Cl8, Technical D039 Tetrachloroethylene chlorinated camphene, 67-69 percent chlorine) D040 Trichlorethylene D016 2,4-D (2,4-Dichlorophenoxyacetic acid) D041 2,4,5-Trichlorophenol D017 2,4,5-TP Silvex (2,4,5- D042 2,4,6-Trichlorophenol Trichlorophenoxypropionic acid) D043 Vinyl chloride D018 Benzene D019 Carbon tetrachloride D020 Chlordane D021 Chlorobenzene D022 Chloroform B-1 EPA HAZARDOUS WASTE CODES (Continued) Code Waste description Code Waste description HAZARDOUS WASTE FROM NONSPECIFIC solvents: cresols, cresylic acid, and SOURCES nitrobenzene; and the still bottoms from the recovery of these solvents; all spent solvent F001 The following spent halogenated solvents mixtures/blends containing, before use, a used in degreasing: Tetrachloroethylene, total of ten percent or more (by volume) of trichlorethylene, methylene chloride, 1,1,1- one or more of the above nonhalogenated trichloroethane, carbon tetrachloride and solvents or those solvents listed in F001, chlorinated fluorocarbons; all spent solvent F002, and F005; and still bottoms from the mixtures/blends used in degreasing recovery of these spent solvents and spent containing, before use, a total of ten solvent mixtures. percent or more (by volume) of one or more of the above halogenated solvents or F005 The following spent nonhalogenated those solvents listed in F002, F004, and solvents: toluene, methyl ethyl ketone, F005; and still bottoms from the recovery carbon disulfide, isobutanol, pyridine, of these spent solvents and spent solvent benzene, 2-ethoxyethanol, and 2- mixtures. nitropropane; all spent solvent mixtures/blends containing, before use, a F002 The following spent halogenated solvents: total of ten percent or more (by volume) of Tetrachloroethylene, methylene chloride, one or more of the above nonhalogenated trichloroethylene, 1,1,1-trichloroethane, solvents or those solvents listed in F001, chlorobenzene, 1,1,2-trichloro-1,2,2- F002, or F004; and still bottoms from the trifluoroethane, ortho-dichlorobenzene, recovery of these spent solvents and spent trichlorofluoromethane, and 1,1,2, solvent mixtures. trichloroethane; all spent solvent mixtures/blends containing, before use, a F006 Wastewater treatment sludges from total of ten percent or more (by volume) of electroplating operations except from the one or more of the above halogenated following processes: (1) sulfuric acid solvents or those solvents listed in F001, anodizing of aluminum; (2) tin plating on F004, and F005; and still bottoms from the carbon steel; (3) zinc plating (segregated recovery of these spent solvents and spent basis) on carbon steel; (4) aluminum or solvent mixtures. zinc-aluminum plating on carbon steel; (5) cleaning/stripping associated with tin, zinc, F003 The following spent non-halogenated and aluminum plating on carbon steel; and solvents: Xylene, acetone, ethyl acetate, (6) chemical etching and milling of ethyl benzene, ethyl ether, methyl isobutyl aluminum. ketone, n-butyl alcohol, cyclohexanone, and methanol; all spent solvent mixtures/ F007 Spent cyanide plating bath solutions from blends containing, before use, only the electroplating operations. above spent nonhalogenated solvents; and all spent solvent mixtures/blends F008 Plating bath residues from the bottom of containing, before use, one or more of the plating baths from electroplating operations above nonhalogenated solvents, and a total in which cyanides are used in the process. of ten percent or more (by volume) of one or more of those solvents listed in F001, F009 Spent stripping and cleaning bath solutions F002, F004, and F005; and still bottoms from electroplating operations in which from the recovery of these spent solvents cyanides are used in the process. and spent solvent mixtures. F010 Quenching bath residues from oil baths F004 The following spent nonhalogenated from metal heat treating operations in B-2 EPA HAZARDOUS WASTE CODES (Continued) Code Waste description Code Waste description which cyanides are used in the process. materials on equipment previously used for the production or manufacturing use (as a F011 Spent cyanide solutions from slat bath pot reactant, chemical intermediate, or cleaning from metal heat treating component in a formulating porcess) of tri- operations. and tetrachlorophenols. (This listing does not include wastes from equipment used F012 Quenching wastewater treatment sludges only for the production or use of from metal heat treating operations in hexachlorophene from highly purified which cyanides are used in the process. 2,4,5-trichlorophenol.) F019 Wastewater treatment sludges from the F024 Process wastes including, but not limited chemical conversion coating of aluminum to, distillation residues, heavy ends, tars, except from zirconium phosphating in and reactor clean-out wastes, from the aluminum can washing when such production of certain chlorinated aliphatic phosphating is an exclusive conversion hydrocarbons by free radical catalyzed coating process. processes. These chlorinated aliphatic hydrocarbons are those having carbon F020 Wastes (except wastewater and spent chain lengths ranging from one to and carbon from hydrogen chloride including five, with varying amounts and purification) from the production or positions of chlorine substitution. (This manufacturing use (as a reactant, chemical listing does not include wastewaters, intermediate, or component in a wastewater treatment sludge, spent formulating process) of tri- or catalysts, and wastes listed in Sections tetrachlorophenol or of intermediates used 261.31. or 261.32) to produce their pesticide derivatives. (This listing does not include wastes from F025 Condensed light ends, spent filters and the production of hexachlorophene from filter aids, and spent desiccant wastes from highly purified 2,4,5-trichlorophenol.) the production of certain chlorinated aliphatic hydrocarbons, by free radical F021 Wastes (except wastewater and spent catalyzed processes. These chlorinated carbon from hydrogen chloride aliphatic hydrocarbons are those having purification) from the production or carbon chain lengths ranging from one, to manufacturing use (as a reactant, chemical and including five, with varying amounts intermediate, or component in a and positions of chlorine substitution. formulating process) of pentachlorophenol, or of intermediates used to produce F026 Wastes (except wastewater and spent derivatives. carbon from hydrogen chloride purification) from the production of F022 Wastes (except wastewater and spent materials on equipment previously used for carbon from hydrogen chloride the manufacturing use (as a reactant, purification) from the manufacturing use chemical intermediate, or component in a (as a reactant, chemical intermediate, or formulating process) of tetra-, penta-, or component in a formulating process) of hexachlorobenzene under alkaline tetra-, penta-, or hexachlorobenzenes under conditions. alkaline conditions. F027 Discarded unused formulations containing F023 Wastes (except wastewater and spent tri-, tetra-, or pentachlorophenol or carbon from hydrogen chloride discarded unused formulations containing purification) from the production of compounds derived from these B-3 EPA HAZARDOUS WASTE CODES (Continued) Code Waste description Code Waste description chlorophenols. (This listing does not F035 Wastewaters, process residuals, include formulations containing preservative drippage, and spent hexachlorophene synthesized from formulations from wood preserving prepurified 2,4,5-trichlorophenol as the sole processes generated at plants that use component.) inorganic preservatives containing arsenic or chromium. This listing does not include F028 Residues resulting from the incineration or K001 bottom sediment sludge from the thermal treatment of soil contaminated with treatment of wastewater from wood EPA hazardous waste nos. F020, F021, preserving processes that use creosote F022, F023, F026, and F027. and/or pentachlorophenol. F032 Wastewaters, process residuals, F037 Petroleum refinery primary oil/water/solids preservative drippage, and spent separation sludge - Any sludge generated formulations from wood preserving from the gravitational separation of processes generated at plants that currently oil/water/solids during the storage or use, or have previously used, treatment of process wastewaters and oily chlorophenolic formulations [except cooling wastewaters from petroleum potentially cross-contaminated wastes that refineries. Such sludges include, but are have had the F032 waste code deleted in not limited to, those generated in accordance with Section 261.35 (i.e., the oil/water/solids separators; tanks and newly promulgated equipment cleaning
Recommended publications
  • Methyl Ethyl Ketone (2-Butanone)
    Methyl Ethyl Ketone (2-Butanone) 78-93-3 Hazard Summary Methyl ethyl ketone is used as a solvent. Acute (short-term) inhalation exposure to methyl ethyl ketone in humans results in irritation to the eyes, nose, and throat. Limited information is available on the chronic (long-term) effects of methyl ethyl ketone in humans. Chronic inhalation studies in animals have reported slight neurological, liver, kidney, and respiratory effects. No information is available on the developmental, reproductive, or carcinogenic effects of methyl ethyl ketone in humans. Developmental effects, including decreased fetal weight and fetal malformations, have been reported in mice and rats exposed to methyl ethyl ketone via inhalation and ingestion. EPA has classified methyl ethyl ketone as a Group D, not classifiable as to human carcinogenicity. Please Note: The main sources of information for this fact sheet are EPA's Health Effects Assessment for Methyl Ethyl Ketone (1) and EPA's Integrated Risk Information System (IRIS) (6), which contains information on inhalation chronic toxicity of methyl ethyl ketone and the RfC and oral chronic toxicity and the RfD. Uses The primary use of methyl ethyl ketone is as a solvent in processes involving gums, resins, cellulose acetate, and cellulose nitrate. (1) Methyl ethyl ketone is also used in the synthetic rubber industry, in the production of paraffin wax, and in household products such as lacquer and varnishes, paint remover, and glues. (1) Sources and Potential Exposure Methyl ethyl ketone has been detected in both indoor and outdoor air. Methyl ethyl ketone can be produced in outdoor air by the photooxidation of certain air pollutants, such as butane and other hydrocarbons.
    [Show full text]
  • 2,4-Dichlorophenoxyacetic Acid
    2,4-Dichlorophenoxyacetic acid 2,4-Dichlorophenoxyacetic acid IUPAC (2,4-dichlorophenoxy)acetic acid name 2,4-D Other hedonal names trinoxol Identifiers CAS [94-75-7] number SMILES OC(COC1=CC=C(Cl)C=C1Cl)=O ChemSpider 1441 ID Properties Molecular C H Cl O formula 8 6 2 3 Molar mass 221.04 g mol−1 Appearance white to yellow powder Melting point 140.5 °C (413.5 K) Boiling 160 °C (0.4 mm Hg) point Solubility in 900 mg/L (25 °C) water Related compounds Related 2,4,5-T, Dichlorprop compounds Except where noted otherwise, data are given for materials in their standard state (at 25 °C, 100 kPa) 2,4-Dichlorophenoxyacetic acid (2,4-D) is a common systemic herbicide used in the control of broadleaf weeds. It is the most widely used herbicide in the world, and the third most commonly used in North America.[1] 2,4-D is also an important synthetic auxin, often used in laboratories for plant research and as a supplement in plant cell culture media such as MS medium. History 2,4-D was developed during World War II by a British team at Rothamsted Experimental Station, under the leadership of Judah Hirsch Quastel, aiming to increase crop yields for a nation at war.[citation needed] When it was commercially released in 1946, it became the first successful selective herbicide and allowed for greatly enhanced weed control in wheat, maize (corn), rice, and similar cereal grass crop, because it only kills dicots, leaving behind monocots. Mechanism of herbicide action 2,4-D is a synthetic auxin, which is a class of plant growth regulators.
    [Show full text]
  • Transport of Dangerous Goods
    ST/SG/AC.10/1/Rev.16 (Vol.I) Recommendations on the TRANSPORT OF DANGEROUS GOODS Model Regulations Volume I Sixteenth revised edition UNITED NATIONS New York and Geneva, 2009 NOTE The designations employed and the presentation of the material in this publication do not imply the expression of any opinion whatsoever on the part of the Secretariat of the United Nations concerning the legal status of any country, territory, city or area, or of its authorities, or concerning the delimitation of its frontiers or boundaries. ST/SG/AC.10/1/Rev.16 (Vol.I) Copyright © United Nations, 2009 All rights reserved. No part of this publication may, for sales purposes, be reproduced, stored in a retrieval system or transmitted in any form or by any means, electronic, electrostatic, magnetic tape, mechanical, photocopying or otherwise, without prior permission in writing from the United Nations. UNITED NATIONS Sales No. E.09.VIII.2 ISBN 978-92-1-139136-7 (complete set of two volumes) ISSN 1014-5753 Volumes I and II not to be sold separately FOREWORD The Recommendations on the Transport of Dangerous Goods are addressed to governments and to the international organizations concerned with safety in the transport of dangerous goods. The first version, prepared by the United Nations Economic and Social Council's Committee of Experts on the Transport of Dangerous Goods, was published in 1956 (ST/ECA/43-E/CN.2/170). In response to developments in technology and the changing needs of users, they have been regularly amended and updated at succeeding sessions of the Committee of Experts pursuant to Resolution 645 G (XXIII) of 26 April 1957 of the Economic and Social Council and subsequent resolutions.
    [Show full text]
  • Methyl Isopropyl Ketone Safety Data Sheet According to Federal Register / Vol
    Methyl isopropyl ketone Safety Data Sheet according to Federal Register / Vol. 77, No. 58 / Monday, March 26, 2012 / Rules and Regulations Date of issue: 05/25/2015 Version: 1.0 SECTION 1: Identification 1.1. Identification Product form : Substance Substance name : Methyl isopropyl ketone CAS-No. : 563-80-4 Product code : (US) W1814 Formula : C5H10O Synonyms : 3-Methylbutane-2-one / Isopropyl methyl ketone / Methyl-2-butanone, 3- / 2-Acetylpropane / 3- Methylbutanone-2 / 3-Methylbutanone / 3-Methylbutan-2-one / 3-Methyl-2-butanone / 2- Butanone, 3-methyl- / Butan-2-one, 3-methyl- 1.2. Recommended use and restrictions on use No additional information available 1.3. S upplie r Synerzine 5340 Hwy 42 S Ellenwood, Georgia 30294 - USA T 404-524-6744 - F 404-577-1651 [email protected] - www.synerzine.com 1.4. Emergency telephone number Emergency number : Infotrac 1-800-535-5053 (Contract# 102471) Dial +1-352-323-3500 when outside the US SECTION 2: Hazard(s) identification 2.1. Classification of the substance or mi xt ure GHS -US classification Flammable liquids Category H225 Highly flammable liquid and vapour 2 Specific target organ toxicity H336 May cause drowsiness or dizziness (single exposure) Category 3 Hazardous to the aquatic H402 Harmful to aquatic life environment - Acute Hazard Category 3 Full text of H statements : see section 16 2.2. GHS Label elements, including precautionary statements GHS-US labeling Hazard pictograms (GHS-US) : Signal word (GHS-US) : Danger Hazard statements (GHS-US) : H225 - Highly flammable liquid and vapour H336 - May cause drowsiness or dizziness H402 - Harmful to aquatic life Precautionary statements (GHS-US) : P210 - Keep away from heat, hot surfaces, sparks, open flames and other ignition sources.
    [Show full text]
  • Toxicological Review of Chloral Hydrate (CAS No. 302-17-0) (PDF)
    EPA/635/R-00/006 TOXICOLOGICAL REVIEW OF CHLORAL HYDRATE (CAS No. 302-17-0) In Support of Summary Information on the Integrated Risk Information System (IRIS) August 2000 U.S. Environmental Protection Agency Washington, DC DISCLAIMER This document has been reviewed in accordance with U.S. Environmental Protection Agency policy and approved for publication. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. Note: This document may undergo revisions in the future. The most up-to-date version will be made available electronically via the IRIS Home Page at http://www.epa.gov/iris. ii CONTENTS—TOXICOLOGICAL REVIEW for CHLORAL HYDRATE (CAS No. 302-17-0) FOREWORD .................................................................v AUTHORS, CONTRIBUTORS, AND REVIEWERS ................................ vi 1. INTRODUCTION ..........................................................1 2. CHEMICAL AND PHYSICAL INFORMATION RELEVANT TO ASSESSMENTS ..... 2 3. TOXICOKINETICS RELEVANT TO ASSESSMENTS ............................3 4. HAZARD IDENTIFICATION ................................................6 4.1. STUDIES IN HUMANS - EPIDEMIOLOGY AND CASE REPORTS .................................................6 4.2. PRECHRONIC AND CHRONIC STUDIES AND CANCER BIOASSAYS IN ANIMALS ................................8 4.2.1. Oral ..........................................................8 4.2.2. Inhalation .....................................................12 4.3. REPRODUCTIVE/DEVELOPMENTAL STUDIES ..........................13
    [Show full text]
  • Chloral Hydrate and Paraldehyde As Drugs of Addiction
    Sept., 1932J CHLORAL HYDRATE DRUG HABIT : CHOPRA & SINGH CHOPRA 481 certain parts of the Punjab. This is not the outcome of the use of the drug in the treatment Original Articles of insomnia, but is due to entirely different causes. Until a few years ago in that province potable country-made spirits were allowed to CHLORAL HYDRATE AND PARALDE' be sold to retail dealers in bulk and the vendors HYDE AS DRUGS OF ADDICTION bottled the liquor themselves. Some of these ingenious people conceived the idea of diluting R. N. m.d. By CHOPRA, m.a., (Cantab.) the spirit and adding small quantities of chloral I.M.S. LIEUTENANT-COLONEL, hydrate to make up for the loss in its potency and which would result from dilution. The know- GURBAKHSH SINGH CHOPRA, m.b., b.s. ledge that the drug had hypnotic and narcotic was obtained from the (Drug Addiction Inquiry, Indian Research Fund effects undoubtedly Association) medical profession and compounders work- in It was further learnt that Series No. 15 ing dispensaries. the effects chloral hydrate in many Chloral produced by hydrate and paraldehyde belong to resemble those by alcohol, the of ways produced group drugs known as soporifics or especially when the latter is taken in large The chief use of hypnotics. this class of drugs quantities. When the two articles are taken is in the treatment of one insomnia, of the together they act in a manner synergistic to worst evils of modern times from which man- each other and in this way the effect of either kind can suffer.
    [Show full text]
  • Past Use of Chlordane, Dieldrin, And
    The Hazard Evaluation and Emergency Response Office (HEER Office) is part of the Hawai‘i Department of Health (HDOH) Environmental Health Administration, whose mission is to protect human health and the environment. The HEER Office provides leadership, support, and partnership in preventing, planning for, responding to, and enforcing environmental laws relating to releases or threats of releases of hazardous substances. Past Use of Chlordane, Dieldrin, and other Organochlorine Pesticides for Termite Control in Hawai‘i: Safe Management Practices around Treated Foundations or during Building Demolition This fact sheet provides building owners, demolition and construction contractors, developers, realtors, and others with an overview of the potential environmental concerns associated with the past use of organochlorine termiticides (pesticides used to control termites) in Hawai‘i. In addition, this fact sheet discusses methods for reducing exposure to organochlorine termiticides during building demolition or around the foundations of treated buildings and identifies resources for further information. What are organochlorine termiticides? Organochlorine termiticides are a group of pesticides that were used for termite control in and around wooden buildings and homes from the mid-1940s to the late 1980s. These organochlorine pesticides included chlordane, aldrin, dieldrin, heptachlor, and dichlorodiphenyltrichloroethane (DDT). They were used primarily by pest control operators in Hawaii’s urban areas, but also by homeowners, the military, the state, and counties to protect buildings against termite damage. In the 1970s and 1980s, the U.S. Environmental Protection Agency (EPA) banned all uses of these organochlorine pesticides except for heptachlor, which can be used today only for control of fire ants in underground power transformers.
    [Show full text]
  • ' ' T UNITED' STATES PATENT 'V OFFICE
    PatentedUNITED’ Apr.v22,_,>1947'-" STATES > PATENT' ‘ 'v TOFFICE ‘2,419,488 " PRODUCTION OF MoNocnLoRo DERIVA- ‘ ~ ' 'rrvns 0F UNSATUBATED NITRILES - ' Harris A. Dutcher, Borg'cr', ‘_Tex_., asslgnor 'to_ 4 Phillips Petroleum Company,.a corporation of ‘.Delaware> f . ' ' > v No Drawing. Application June 5,1944, I, > Serial No. 538,880 ‘ , ' 11 Claims. (01. zed-464$ , . 2 . The present invention relates to the production - Heretofore, a-chloroacrylonitrile has been pro of chlorine derivatives of unsaturated nitriles by ' duced as a by-product oi.‘ the direct substitutive the reaction of acetylene or acetylenic hydrocar- chlorination of acrylonitrile in the vapor phase bons with cyanogen chloride. More particularly over active carbon at a temperature between ap the invention relates to the production of 3- 5 proximately 200° and approximately 550° C. chloroacrylonitrile - ‘ . (Long, U. S. Patent No. 2,231,363). The process (Z-chloroviny] cyanide,‘ C1__CH___CH_CN) yields 2-chloroacrylonitrile as the principal prod uct. vNo other methods for the production of 3 rgldsl?ltlgfesmigoilxgr196ii?ggtggesagty‘gfgtg; chloroacrylonitrile or other monochloro deriva acetylenic hydrocarbons and cyanogen chloride 10 tives of unsaturatednitriles are known. ‘ ' ’ I have found that acetylene and acetylenic hy is 2281322232”; ‘13355;:ffgléetggesggtdilrgggi? . drocarbons may be reacted with cyanogen halides . I . v to produce.monohalogen-substituted unsaturated monochloro derivatives of unsaturated mtnles, . 1 such as 3-chloroacrylonitrile by there'action of- 1 mtr?es' The reactlon 1.5 facihtated ‘by certain ’ - » >15 catalysts which are referred to more speci?cally acetylene and cyanogen chloride. , hereinafter _ provideAnother a categlyst ob'ect (1201‘f thpfoggtiiirgtthevggg?lo?rg- e ‘n ' ' ‘ o Cyanogen' ‘ihlmd‘?. 157a readny.condens1ble.
    [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]
  • EPA Listed Wastes Table 1: Maximum Concentration of Contaminants For
    EPA Listed Wastes Table 1: Maximum concentration of contaminants for the toxicity characteristic, as determined by the TCLP (D list) Regulatory HW No. Contaminant CAS No. Level (mg/L) D004 Arsenic 7440-38-2 5.0 D005 Barium 7440-39-3 100.0 D0018 Benzene 71-43-2 0.5 D006 Cadmium 7440-43-9 1.0 D019 Carbon tetrachloride 56-23-5 0.5 D020 Chlordane 57-74-9 0.03 D021 Chlorobenzene 108-90-7 100.0 D022 Chloroform 67-66-3 6.0 D007 Chromium 7440-47-3 5.0 D023 o-Cresol 95-48-7 200.0** D024 m-Cresol 108-39-4 200.0** D025 p-Cresol 106-44-5 200.0** D026 Cresol ------------ 200.0** D016 2,4-D 94-75-7 10.0 D027 1,4-Dichlorobenzene 106-46-7 7.5 D028 1,2-Dichloroethane 107-06-2 0.5 D029 1,1-Dichloroethylene 75-35-4 0.7 D030 2,4-Dinitrotoluene 121-14-2 0.13* D012 Endrin 72-20-8 0.02 D031 Heptachlor 76-44-8 0.008 D032 Hexachlorobenzene 118-74-1 0.13* D033 Hexachlorobutadiene 87-68-3 0.5 D034 Hexachloroethane 67-72-1 3.0 D008 Lead 7439-92-1 5.0 D013 Lindane 58-89-9 0.4 D009 Mercury 7439-97-6 0.2 D014 Methoxychlor 72-43-5 10.0 D035 Methyl ethyl ketone 78-93-3 200.0 D036 Nitrobenzene 98-95-3 2.0 D037 Pentachlorophenol 87-86-5 100.0 D038 Pyridine 110-86-1 5.0* D010 Selenium 7782-49-2 1.0 D011 Silver 7740-22-4 5.0 D039 Tetrachloroethylene 127-18-4 0.7 D015 Toxaphene 8001-35-2 0.5 D040 Trichloroethylene 79-01-6 0.5 D041 2,4,5-Trichlorophenol 95-95-4 400.0 D042 2,4,6-Trichlorophenol 88-06-2 2.0 D017 2,4,5-TP (Silvex) 93-72-1 1.0 D043 Vinyl Chloride 74-01-4 0.2 * Quantitation limit is greater than the calculated regulatory level.
    [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]