Committee for Risk Assessment RAC Opinion on Arsenic Acid and Its

Total Page:16

File Type:pdf, Size:1020Kb

Committee for Risk Assessment RAC Opinion on Arsenic Acid and Its Committee for Risk Assessment RAC Opinion on Arsenic acid and its inorganic salts ECHA/RAC/A77-O-0000001412-86-148/F Adopted 29 May 2017 Annankatu 18, P.O. Box 400, FI-00121 Helsinki, Finland | Tel. +358 9 686180 | Fax +358 9 68618210 | echa.europa.eu 2 RAC Opinion 29 May 2017 ECHA/RAC/A77-O-0000001412-86-148/F OPINION OF THE COMMITTEE FOR RISK ASSESSMENT ON THE EVALUATION OF THE OCCUPATIONAL EXPOSURE LIMITS (OELs) FOR ARSENIC ACID AND ITS INORGANIC SALTS Pursuant to Article 77(3)(c) of Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006 concerning the Registration, Evaluation, Authorisation and Restriction of Chemicals (the REACH Regulation), the Committee for Risk Assessment (RAC) has adopted an opinion on the evaluation of the scientific relevance of occupational exposure limits (OELs) for arsenic acid and its inorganic salts. Commission request The Commission, in view of the preparation of the third and fourth proposal for an amendment of Directive 2004/37/EC on the protection of workers from the risks related to exposure to carcinogens or mutagens at work (CMD), and in line with the 2017 Commission Communication ‘Safer and Healthier Work for All’ - Modernisation of the EU Occupational Safety and Health Legislation and Policy’1, has decided to ask the advice of RAC to assess the scientific relevance of occupational exposure limits for some carcinogenic chemical substances. Therefore, the Commission has made a request (8 March 20172) in accordance with Article 77 (3)(c) of the REACH Regulation, to evaluate, in accordance with Directive 98/24/EC on the protection of the health and safety of workers from the risks related to chemical agents at work (CAD) and/or Directive 2004/37/EC on the protection of workers from the risks related to exposure to carcinogens or mutagens at work (CMD), the following chemical compounds: 4,4'-methylenebis[2-chloroaniline] (MOCA), arsenic acid and its inorganic salts, nickel and its compounds, acrylonitrile and benzene. I PROCESS FOR ADOPTION OF THE OPINION Following a request from the European Commission, in the mandate of 15 March 20173, the Executive Director of ECHA requested RAC to draw up an opinion on the evaluation of the scientific relevance of occupational exposure limits (OELs) for arsenic acid and its inorganic salts. The aim of the opinion is to provide scientific advice in support of the Commission action on the Proposal to amend Directive 2004/37/EC (3rd wave of amendment). This advice must include a recommendation to be given to the Advisory Committee on Safety and Health at Work (ACSH) in line with the relevant OSH legislative procedures and in the format used by SCOEL in drafting its opinion. An initial proposal was prepared by the European Chemicals Agency for the consideration by RAC. The current opinion was reviewed by RAC in a written commenting round from 05 May 2017 to 23 May 2017 and at the RAC-41 meeting,. Due to imposed time constraints, the opinion was not subject to a Public Consultation. 1 http://ec.europa.eu/social/main.jsp?langId=en&catId=148&newsId=2709&furtherNews=yes 2 https://echa.europa.eu/documents/10162/13641/ec_note_to_echa_oels_en.pdf/f72342ef-7361- 0d7c-70a1-e77243bdc5c1 3 https://echa.europa.eu/documents/10162/13641/rac_mandate_oels_en.pdf/9f9b7fb9-545a- 214c-69f0-dff5f5092174 RAC Opinion 3 II ADOPTION OF THE OPINION OF THE RAC Rapporteur, appointed by the RAC: Tiina Santonen. The RAC opinion was adopted by consensus on 29 May 2017.… 4 RAC Opinion Table of Contents RECOMMENDATION ............................................................................................ 8 SUMMARY TABLE ............................................................................................ 8 SUMMARY ..................................................................................................... 9 REPORT ............................................................................................................ 13 1. CHEMICAL AGENT IDENTIFICATION AND PHYSICO-CHEMICAL PROPERTIES .......... 13 2. EU HARMONISED CLASSIFICATION AND LABELLING - CLP (EC)1271/2008 ........... 15 3. CHEMICAL AGENT AND SCOPE OF LEGISLATION - REGULATED USES OF ARSENIC ACID AND ITS SALTS IN THE EU .......................................................................... 17 3.1 DIRECTIVE 98/24/EC AND DIRECTIVE 2004/37/EC ....................................... 17 3.2 REACH REGISTRATIONS (2010 AND 2013) .................................................. 18 3.3 AUTHORISED USES UNDER ANNEX XIV OF REACH ........................................ 19 3.4 RESTRICTED USES UNDER ANNEX XVII OF REACH ....................................... 20 3.5 PLANT PROTECTION PRODUCTS REGULATION (EC)1107/2009 ....................... 20 3.6 BIOCIDAL PRODUCTS REGULATION (EU)528/2012 ....................................... 21 4. EXISTING OCCUPATIONAL EXPOSURE LIMITS .................................................... 21 5. OCCURRENCE, USE AND OCCUPATIONAL EXPOSURE .......................................... 22 5.1 OCCURRENCE ........................................................................................... 22 5.2 PRODUCTION AND USE INFORMATION ........................................................ 23 5.3 OCCUPATIONAL EXPOSURE ........................................................................ 27 5.3.1 General exposure ............................................................................. 27 5.3.2 Occupational exposure from uses and processes relevant to arsenic acid and its compounds ................................................................................ 28 5.4 ROUTES OF EXPOSURE AND UPTAKE ........................................................... 37 5.4.1 Worker exposure .............................................................................. 37 5.4.2 General population ........................................................................... 37 6. MONITORING EXPOSURE ................................................................................. 38 6.1 EXTERNAL EXPOSURE ............................................................................... 38 6.2 BIOMONITORING OF EXPOSURE (INTERNAL EXPOSURE) ............................... 39 7. HEALTH EFFECTS ........................................................................................... 42 7.1 TOXICOKINETICS (ABSORPTION, DISTRIBUTION, METABOLISM AND EXCRETION - ADME) ................................................................................................ 42 7.1.1 Human data .................................................................................... 42 7.1.2 Animal data ..................................................................................... 44 7.1.3 In vitro data .................................................................................... 44 RAC Opinion 5 7.1.4 Toxicokinetic modelling ..................................................................... 44 7.1.5 Biological monitoring ........................................................................ 45 7.2 ACUTE TOXICITY ...................................................................................... 49 7.2.1 Human data .................................................................................... 49 7.2.2 Animal data ..................................................................................... 49 7.2.3 In vitro data .................................................................................... 50 7.2.4 Summary ........................................................................................ 50 7.3 SPECIFIC TARGET ORGAN TOXICITY/REPEATED DOSE TOXICITY .................... 50 7.3.1 Human data .................................................................................... 50 7.3.2 Animal data ..................................................................................... 51 7.3.3 Summary ........................................................................................ 52 7.4 IRRITANCY AND CORROSIVITY ................................................................... 52 7.4.1 Human data .................................................................................... 52 7.4.2 Local effects on the eyes are often characterised by conjunctivitis, often in combination with facial dermatitis [82], [86] (LG, 1921; Pinto et al, 1953) .Animal data .................................................................................. 52 7.4.3 Summary ........................................................................................ 52 7.5 EXPOSURE TO ARSENIC DUSTS CAUSES IRRITATION TO THE RESPIRATORY SYSTEM AND DERMAL CONTACT CAN CAUSE IRRITATION AND DERMATITIS. SENSITISATION ................................................................................... 52 7.5.1 Human data .................................................................................... 53 7.5.2 Animal data ..................................................................................... 53 7.5.3 Summary ........................................................................................ 53 7.6 GENOTOXICITY ........................................................................................ 53 7.6.1 Human data .................................................................................... 53 7.6.2 Animal data ..................................................................................... 54 7.6.3 In vitro data .................................................................................... 54 7.6.4 Summary .......................................................................................
Recommended publications
  • A Guide to Export Controls
    Foreign Affairs, Trade and Affaires étrangères, Commerce et Development Canada Développment Canada A Guide To CANADA’S EXPORT CONTROLS December 2012 Introduction The issuance of export permits is administered by the Export Controls Division (TIE) of Foreign Affairs, Trade and Development Canada (DFATD). TIE provides assistance to exporters in determining if export permits are required. It also publishes brochures and Notices to Exporters that are freely available on request and on our website www.exportcontrols.gc.ca. How to contact us: Export Controls Division (TIE) Foreign Affairs, Trade and Development Canada 111 Sussex Drive Ottawa, Ontario K1A 0G2 Telephone: (613) 996-2387 Facsimile: (613) 996-9933 Email: [email protected] For information on how to apply for an export permit and additional information on export controls please refer to our website. To enquire on the status of an export permit application: Recognized EXCOL users can check the status of an export permit application on-line. Non-recognized users can call (613) 996-2387 or email [email protected] and quote your export permit application identification (ref ID) number. Export Controls Division website: www.exportcontrols.gc.ca This Guide, at time of publication, encompasses the list of items enumerated on the Export Control List (ECL) that are controlled for export in accordance with Canadian foreign policy, including Canada’s participation in multilateral export control regimes and bilateral agreements. Unless otherwise specified, the export controls contained in this Guide apply to all destinations except the United States. Canada’s Export Control List can be found at the Department of Justice website at http://canada.justice.gc.ca/.
    [Show full text]
  • The Calcium Arsenates
    Station RuIletin 131. June, 1918 Oregon Agricultural College Experiment Station AGRICULTURAL CHEMISTRY DEPARTMENT The Calcium Arsenates By R. H. ROBINSON Acting Chemist, Oregon Agricultural Experiment Station. CORVALLIS, OREGON The regular huIlejne of the Station are sent free to the residents of Oregon who request them. THE CALCIUM ARSENATES By R. H. ROBINSON Acting Chemist, Oregon Agricultural Experiment Station INTRODUCTION Chemical investigations on the calcium arsenates relative to their economfic value and practicability as insecticides have been carried on by the department of Agricultural Chemistry of this Station during the past two years.The results obtained from these investigations are presented in this bulletin.The work was supported by the annual funds provided by the Adams Act of the United States Government.. Commercial calcium arsenate is an arsenical now being produced by reliable manufacturers of spray material and offered for sale as a sub- stitute for the arsenates of lead.The value of the latter as a stomachic insecticide has been demonstrated, and itis now used extensively for the successful controlof the codling moth, the destructionof the cotton boll worm., the tobacco worm, and the Colorado potato beetle. Previous inveatigations on the toxic values and killing power of calcium arsenate and lead arsenate indicate equal efficiency. A consideration of a few figures will show the economic advantages which might be gained if calcium arsenate could be substituted for lead arsenate.A conservative estimate of the quantity of lead arsenate used annually in the United States, as stated by one of the largest manufac- turers of spray materials, is probably more than 30,000,000 pounds.
    [Show full text]
  • Arsenic Summary & Details: Greenfacts
    http://www.greenfacts.org/ Copyright © GreenFacts page 1/9 Scientific Facts on Source document: IPCS (2001) Arsenic Summary & Details: GreenFacts Level 2 - Details on Arsenic 1. What is arsenic?.............................................................................................................3 1.1 What are the properties of arsenic?...................................................................................3 1.2 How are arsenic levels measured?.....................................................................................3 2. Where does environmental arsenic come from?....................................................3 2.1 What are the natural sources of environmental arsenic?.......................................................3 2.2 What are the man-made sources of environmental arsenic?..................................................4 2.3 How is arsenic transported and distributed in the environment?............................................4 3. What are the levels of exposure to arsenic?...........................................................4 3.1 How much arsenic is there in the environment?..................................................................4 3.2 What levels of arsenic are found in living organisms?...........................................................5 3.3 What levels of arsenic are humans exposed to?..................................................................5 4. What happens to arsenic in the body?......................................................................6 4.1
    [Show full text]
  • Use of Fluorescence to Guide Resection Or Biopsy of Primary Brain Tumors and Brain Metastases
    Neurosurg Focus 36 (2):E10, 2014 ©AANS, 2014 Use of fluorescence to guide resection or biopsy of primary brain tumors and brain metastases *SERGE MARBACHER, M.D., M.SC.,1,5 ELISABETH KLINGER, M.D.,2 LUCIA SCHWYZER, M.D.,1,5 INGEBORG FISCHER, M.D.,3 EDIN NEVZATI, M.D.,1 MICHAEL DIEPERS, M.D.,2,5 ULRICH ROELCKE, M.D.,4,5 ALI-REZA FATHI, M.D.,1,5 DANIEL COLUCCIA, M.D.,1,5 AND JAVIER FANDINO, M.D.1,5 Departments of 1Neurosurgery, 2Neuroradiology, 3Pathology, and 4Neurology, and 5Brain Tumor Center, Kantonsspital Aarau, Aarau, Switzerland Object. The accurate discrimination between tumor and normal tissue is crucial for determining how much to resect and therefore for the clinical outcome of patients with brain tumors. In recent years, guidance with 5-aminolev- ulinic acid (5-ALA)–induced intraoperative fluorescence has proven to be a useful surgical adjunct for gross-total resection of high-grade gliomas. The clinical utility of 5-ALA in resection of brain tumors other than glioblastomas has not yet been established. The authors assessed the frequency of positive 5-ALA fluorescence in a cohort of pa- tients with primary brain tumors and metastases. Methods. The authors conducted a single-center retrospective analysis of 531 patients with intracranial tumors treated by 5-ALA–guided resection or biopsy. They analyzed patient characteristics, preoperative and postoperative liver function test results, intraoperative tumor fluorescence, and histological data. They also screened discharge summaries for clinical adverse effects resulting from the administration of 5-ALA. Intraoperative qualitative 5-ALA fluorescence (none, mild, moderate, and strong) was documented by the surgeon and dichotomized into negative and positive fluorescence.
    [Show full text]
  • United States Patent (19) (11) 4,161,571 Yasui Et Al
    United States Patent (19) (11) 4,161,571 Yasui et al. 45 Jul. 17, 1979 (54) PROCESS FOR PRODUCTION OF THE 4,080,493 3/1978 Yasui et al. .......................... 260/879 MALE CANHYDRDE ADDUCT OF A 4,082,817 4/1978 Imaizumi et al. ...................... 526/46 LIQUID POLYMER 4,091,198 5/1978 Smith ..................................... 526/56 75 Inventors: Seimei Yasui, Takarazuka; Takao FOREIGN PATENT DOCUMENTS Oshima, Sonehigashi, both of Japan 2262677 2/1975 France ....................................... 526/56 73) Assignee: Sumitomo Chemical Company, 44-1989 1/1969 Japan ......................................... 526/56 Limited, Osaka, Japan Primary Examiner-William F. Hamrock Attorney, Agent, or Firm-Birch, Stewart, Kolasch and 21 Appl. No.: 843,311 Birch 22 Filed: Oct. 18, 1977 57 ABSTRACT Related U.S. Application Data A process for production of the maleic anhydride ad duct of a liquid polymer having a maleic anhydride 62 Division of Ser. No. 733,914, Oct. 19, 1976, Pat, No. addition amount of 2 to 70% by weight, which com 4,080,493. prises reacting a liquid polymer having a molecular 51 Int. C.’................................................ CO8F 8/46 weight of 150 to 5,000 and a viscosity of 2 to 50,000 cp (52) U.S. C. ...................................... 526/90; 526/192; at 30 C. in the presence of at least one compound, as a 526/209; 526/213; 526/193; 526/195; 526/226; gelation inhibitor, selected from the group consisting of 526/233; 526/237; 526/238; 526/272; 525/285; imidazoles, thiazoles, metallic salts of mercapto 525/249; 525/251; 525/255; 525/245; 525/248 thiazoles, urea derivatives, naphthylamines, nitrosa (58) Field of Search ................
    [Show full text]
  • Arsenic Trioxide Is Highly Cytotoxic to Small Cell Lung Carcinoma Cells
    160 Arsenic trioxide is highly cytotoxic to small cell lung carcinoma cells 1 1 Helen M. Pettersson, Alexander Pietras, effect of As2O3 on SCLC growth, as suggested by an Matilda Munksgaard Persson,1 Jenny Karlsson,1 increase in neuroendocrine markers in cultured cells. [Mol Leif Johansson,2 Maria C. Shoshan,3 Cancer Ther 2009;8(1):160–70] and Sven Pa˚hlman1 1Center for Molecular Pathology, CREATE Health and 2Division of Introduction Pathology, Department of Laboratory Medicine, Lund University, 3 Lung cancer is the most frequent cause of cancer deaths University Hospital MAS, Malmo¨, Sweden; and Department of f Oncology-Pathology, Cancer Center Karolinska, Karolinska worldwide and results in 1 million deaths each year (1). Institute and Hospital, Stockholm, Sweden Despite novel treatment strategies, the 5-year survival rate of lung cancer patients is only f15%. Small cell lung carcinoma (SCLC) accounts for 15% to 20% of all lung Abstract cancers diagnosed and is a very aggressive malignancy Small cell lung carcinoma (SCLC) is an extremely with early metastatic spread (2). Despite an initially high aggressive form of cancer and current treatment protocols rate of response to chemotherapy, which currently com- are insufficient. SCLC have neuroendocrine characteristics bines a platinum-based drug with another cytotoxic drug and show phenotypical similarities to the childhood tumor (3, 4), relapses occur in the absolute majority of SCLC neuroblastoma. As multidrug-resistant neuroblastoma patients. At relapse, the efficacy of further chemotherapy is cells are highly sensitive to arsenic trioxide (As2O3) poor and the need for alternative treatments is obvious. in vitro and in vivo, we here studied the cytotoxic effects Arsenic-containing compounds have been used in tradi- of As2O3 on SCLC cells.
    [Show full text]
  • APPENDIX G Acid Dissociation Constants
    harxxxxx_App-G.qxd 3/8/10 1:34 PM Page AP11 APPENDIX G Acid Dissociation Constants §␮ ϭ 0.1 M 0 ؍ (Ionic strength (␮ † ‡ † Name Structure* pKa Ka pKa ϫ Ϫ5 Acetic acid CH3CO2H 4.756 1.75 10 4.56 (ethanoic acid) N ϩ H3 ϫ Ϫ3 Alanine CHCH3 2.344 (CO2H) 4.53 10 2.33 ϫ Ϫ10 9.868 (NH3) 1.36 10 9.71 CO2H ϩ Ϫ5 Aminobenzene NH3 4.601 2.51 ϫ 10 4.64 (aniline) ϪO SNϩ Ϫ4 4-Aminobenzenesulfonic acid 3 H3 3.232 5.86 ϫ 10 3.01 (sulfanilic acid) ϩ NH3 ϫ Ϫ3 2-Aminobenzoic acid 2.08 (CO2H) 8.3 10 2.01 ϫ Ϫ5 (anthranilic acid) 4.96 (NH3) 1.10 10 4.78 CO2H ϩ 2-Aminoethanethiol HSCH2CH2NH3 —— 8.21 (SH) (2-mercaptoethylamine) —— 10.73 (NH3) ϩ ϫ Ϫ10 2-Aminoethanol HOCH2CH2NH3 9.498 3.18 10 9.52 (ethanolamine) O H ϫ Ϫ5 4.70 (NH3) (20°) 2.0 10 4.74 2-Aminophenol Ϫ 9.97 (OH) (20°) 1.05 ϫ 10 10 9.87 ϩ NH3 ϩ ϫ Ϫ10 Ammonia NH4 9.245 5.69 10 9.26 N ϩ H3 N ϩ H2 ϫ Ϫ2 1.823 (CO2H) 1.50 10 2.03 CHCH CH CH NHC ϫ Ϫ9 Arginine 2 2 2 8.991 (NH3) 1.02 10 9.00 NH —— (NH2) —— (12.1) CO2H 2 O Ϫ 2.24 5.8 ϫ 10 3 2.15 Ϫ Arsenic acid HO As OH 6.96 1.10 ϫ 10 7 6.65 Ϫ (hydrogen arsenate) (11.50) 3.2 ϫ 10 12 (11.18) OH ϫ Ϫ10 Arsenious acid As(OH)3 9.29 5.1 10 9.14 (hydrogen arsenite) N ϩ O H3 Asparagine CHCH2CNH2 —— —— 2.16 (CO2H) —— —— 8.73 (NH3) CO2H *Each acid is written in its protonated form.
    [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]
  • The Insecticide Industry of Today Seed Production in Various States Has Comprises More Than 50 Basic Producers Doubled the Yield
    put nearly 2 million dollars extra in the growers' pockets. In Mississippi at least 75 percent of the 1950 cotton crop The Insecticide would have been destroyed were it not for the control of insects through the Industry use of the industry's products. Insecti- cides applied in Nebraska to control Lea S. Hitchner grasshoppers in 1949 resulted in savings estimated at 2 million dollars. Insecti- cidal treatment of alfalfa raised for The insecticide industry of today seed production in various States has comprises more than 50 basic producers doubled the yield. or manufacturers and more than 500 One factor among others responsible formulatorsj xemixers, and processors. for the high productivity of American From their plants throughout the coun- agriculture is the cooperative attack try comes a great variety of insecticides that is waged on insects and other pests. and related products. The agricultural chemicals industry The products, except those derived has welcomed the opportunity to co- from botanical sources, have their ori- operate with Federal and State agen- gins in the basic chemicals on which cies and with farm organizations in this the industry is founded, but the proc- important work and to carry the re- esses that turn the raw materials into sponsibility for developing, producing, the finished products applied by farm- and delivering the necessary pesticides. ers are long, highly scientific, and ex- Such a responsibility is a heavy one pensive in capital. investment and even in normal times. It becomes operating costs. acutely heavy in times of national The industry employs thousands of stress, when shortages of raw materials, scientists in the fields of entomology, containers, personnel, and transporta- plant pathology, botany, toxicology, tion may hamper production and dis- medicine, chemistry, and chemical en- tribution.
    [Show full text]
  • Chromium, Copper and Arsenic Oxide)-Treated Wood Hata, T.; Bronsveld, Paulus; Vystavel, T.; Kooi, Bart; De Hosson, J.T.M.; Kakitani, T.; Otono, A.; Imamura, Y
    University of Groningen Electron microscopic study on pyrolysis of CCA (chromium, copper and arsenic oxide)-treated wood Hata, T.; Bronsveld, Paulus; Vystavel, T.; Kooi, Bart; De Hosson, J.T.M.; Kakitani, T.; Otono, A.; Imamura, Y. Published in: Journal of Analytical and Applied Pyrolysis DOI: 10.1016/S0165-2370(03)00077-9 IMPORTANT NOTE: You are advised to consult the publisher's version (publisher's PDF) if you wish to cite from it. Please check the document version below. Document Version Publisher's PDF, also known as Version of record Publication date: 2003 Link to publication in University of Groningen/UMCG research database Citation for published version (APA): Hata, T., Bronsveld, P. M., Vystavel, T., Kooi, B. J., de Hosson, J. T. M., Kakitani, T., ... Imamura, Y. (2003). Electron microscopic study on pyrolysis of CCA (chromium, copper and arsenic oxide)-treated wood. Journal of Analytical and Applied Pyrolysis, 68-9(1), 635-643. DOI: 10.1016/S0165-2370(03)00077-9 Copyright Other than for strictly personal use, it is not permitted to download or to forward/distribute the text or part of it without the consent of the author(s) and/or copyright holder(s), unless the work is under an open content license (like Creative Commons). Take-down policy If you believe that this document breaches copyright please contact us providing details, and we will remove access to the work immediately and investigate your claim. Downloaded from the University of Groningen/UMCG research database (Pure): http://www.rug.nl/research/portal. For technical reasons the number of authors shown on this cover page is limited to 10 maximum.
    [Show full text]
  • Table 2. Acute Dose-Response Values for Screening Risk Assessments
    Date: 6/18/2018 Revisions since 9/18/2014 are shown in red. Table 2. Acute Dose-Response Values for Screening Risk Assessments. MRL = ATSDR minumum risk levels for no adverse effects for 1 to 14-day exposures. REL = California EPA reference exposure level for no adverse effects. Most, but not all, RELs are for 1-hour exposures. AEGL = Acute exposure guideline levels for mild effects (AEGL-1) and moderate effects (AEGL-2) for 1- and 8-hour exposures. Superscripts indicate the AEGL's status: f = final, i=interim, and p=proposed. ERPG = US DOE Emergency Removal Program guidelines for mild or transient effects (ERPG-1) and irreversible or serious effects (ERPG-2) for 1-hour exposures. IDLH/10 = One-tenth of levels determined by NIOSH to be imminently dangerous to life and health, approximately comparable to mild effects levels for 1-hour exposures. IDLH/10 values shown here are only for substances that lack AEGL and ERPG values. TEEL = US DOE Temporary emergency exposure limits for mild, transient effects (TEEL-1) for 1-hour exposures. TEELs are derived according to a tiered, formula-like methodology, and do not undergo peer review. They are not recommended as the basis for regulatory desision-making, and are shown here only to inform situations where acute values from other sources are not available. Table 2. Acute Dose-Response Values for Screening Risk Assessments MRL REL AEGL-1 (1-h) AEGL-1 (8-h) AEGL-2 (1-h) AEGL-2 (8-h) ERPG-1 ERPG-2 IDLH/10 TEEL-1 CHEMICAL NAME CAS NO.
    [Show full text]
  • CHEM 301 Assignment #2 Provide Solutions to the Following Questions in a Neat and Well-Organized Manner
    CHEM 301 Assignment #2 Provide solutions to the following questions in a neat and well-organized manner. Reference data sources for any constants and state assumptions, if any. Due date: Thursday, Oct 20th, 2016 Attempt all questions. Only even numbers will be assessed. 1. A pond in an area affected by acid mine drainage is observed to have freshly precipitated Fe(OH)3(s) at pH 4. What is the minimum value of pe in this water? Use the appropriate pe-pH speciation diagram to predict the dominant chemical speciation of carbon, sulfur and copper under these conditions. 2. The solubility of FeS(s) in marine sediments is expected to be affected by the pH and the [H2S(aq)] in the surrounding pore water? Calculate the equilibrium concentration of Fe2+ (ppb) at pH 5 and pH 8, -3 assuming the H2S is 1.0 x 10 M. pKsp(FeS) = 16.84. + 2+ FeS(s) + 2 H (aq) ==== Fe (aq) + H2S 3. Boric acid is a triprotic acid (H3BO3); pKa1 = 9.24, pKa2 = 12.74 and pKa3 = 13.80. a) Derive an expression for the fractional abundance of H3BO3 as a function of pH b) Construct a fully labeled pH speciation diagram for boric acid over the pH range of 0 to 14 using Excel spreadsheet at a 0.2 pH unit interval. 4. At pCl- = 2.0, Cd2+ and CdCl+ are the only dominant cadmium chloride species with a 50% fractional abundance of each. + a) Calculate the equilibrium constant for the formation of CdCl (1). + - b) Derive an expression for the fractional abundance of CdCl as a function of [Cl ] and 1 – 4 for cadmium chloro species.
    [Show full text]