Arsenic and Arsenic Compounds
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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. -
Identification and Quantification of Arsenic Species in Gold Mine Wastes Using Synchrotron-Based X-Ray Techniques
Identification and Quantification of Arsenic Species in Gold Mine Wastes Using Synchrotron-Based X-ray Techniques Andrea L. Foster, PhD U.S. Geological Survey GMEG Menlo Park, CA Arsenic is an element of concern in mined gold deposits around the world Spenceville (Cu-Au-Ag) Lava Cap (Nevada) Ketza River (Au) Empire Mine (Nevada) low-sulfide, qtz Au sulfide and oxide ore Argonaut Mine (Au) bodies Don Pedro Harvard/Jamestown Ruth Mine (Cu) Kelly/Rand (Au/Ag) Goldenville, Caribou, and Montague (Au) The common arsenic-rich particles in hard-rock gold mines have long been known Primary Secondary Secondary/Tertiary Iron oxyhydroxide (“rust”) “arsenian” pyrite containing arsenic up to 20 wt% -1 Scorodite FeAsO 2H O As pyrite Fe(As,S)2 4 2 Kankite : FeAsO4•3.5H2O Reich and Becker (2006): maximum of 6% As-1 Arseniosiderite Ca2Fe3(AsO4)3O2·3H2O Arsenopyrite FeAsS Jarosite KFe3(SO4)2(OH)6 Yukonite Ca7Fe12(AsO4)10(OH)20•15H2O Tooleite [Fe6(AsO3)4(SO4)(OH)4•4H2O Pharmacosiderite KFe (AsO ) (OH) •6–7H O arsenide n- 4 4 3 4 2 n = 1-3 But it is still difficult to predict with an acceptable degree of uncertainty which forms will be present • thermodynamic data lacking or unreliable for many important phases • kinetic barriers to equilibrium • changing geochemical conditions (tailings management) Langmuir et al. (2006) GCA v70 Lava Cap Mine Superfund Site, Nevada Cty, CA Typical exposure pathways at arsenic-contaminated sites are linked to particles and their dissolution in aqueous fluids ingestion of arsenic-bearing water dissolution near-neutral, low -
Arsenic and Lead Contamination in Oklahoma Soils Arsenic and Lead Are Naturally Occurring Elements Present in Rocks
Arsenic and Lead Contamination in Oklahoma Soils Arsenic and lead are naturally occurring elements present in rocks. As these rocks erode, arsenic and lead get in soils, waters and plants. The United States Geological Survey (USGS) reports an average of 7.4 parts per million (ppm) as the arsenic concentration in soils for the entire United States and 7.2 ppm as the average arsenic concentration in soils for the western U.S.(1) Background arsenic concentrations in Central Oklahoma soils range from 0.6 to 21 ppm.(2) The USGS reports an average lead concentration of 13 parts per million (ppm) in soils for central Oklahoma(2) and an average lead concentration of 18 ppm for the Western United States.(3) Pollution from historic lead and zinc smelters in Oklahoma left residues of lead, arsenic and cadmium in area soils. Contamination was also spread by using smelter debris as fill material, driveways and roads. These former smelters were primarily located in eastern Oklahoma. Some arsenic contamination above naturally occurring levels is also attributed to agricultural, energy and industrial practices. For example, arsenic-containing insecticides and herbicides were widely used on vegetables, fruits and field crops from the 1900s to around 1950. Coal combustion, wood preserving and smelting operations are known to be sources of arsenic contamination.(1) Lead was once commonly used in paint and in plumbing. Lead was an additive to gasoline for many years and has also been found in ceramics, mini-blinds and other products. Homes built before 1970 commonly have lead-based paint. Renovation activities and peeling or flaking paint can release lead inside the home. -
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. -
An Investigation of the Crystal Growth of Heavy Sulfides in Supercritical
AN ABSTRACT OF THE THESIS OF LEROY CRAWFORD LEWIS for the Ph. D. (Name) (Degree) in CHEMISTRY presented on (Major) (Date) Title: AN INVESTIGATION OF THE CRYSTAL GROWTH OF HEAVY SULFIDES IN SUPERCRITICAL HYDROGEN SULFIDE Abstract approved Redacted for privacy Dr. WilliarriIJ. Fredericks Solubility studies on the heavy metal sulfides in liquid hydrogen sulfide at room temperature were carried out using the isopiestic method. The results were compared with earlier work and with a theoretical result based on Raoult's Law. A relative order for the solubilities of sulfur and the sulfides of tin, lead, mercury, iron, zinc, antimony, arsenic, silver, and cadmium was determined and found to agree with the theoretical result. Hydrogen sulfide is a strong enough oxidizing agent to oxidize stannous sulfide to stannic sulfide in neutral or basic solution (with triethylamine added). In basic solution antimony trisulfide is oxi- dized to antimony pentasulfide. In basic solution cadmium sulfide apparently forms a bisulfide complex in which three moles of bisul- fide ion are bonded to one mole of cadmium sulfide. Measurements were made extending the range over which the volumetric properties of hydrogen sulfide have been investigated to 220 °C and 2000 atm. A virial expression in density was used to represent the data. Good agreement, over the entire range investi- gated, between the virial expressions, earlier work, and the theorem of corresponding states was found. Electrical measurements were made on supercritical hydro- gen sulfide over the density range of 10 -24 moles per liter and at temperatures from the critical temperature to 220 °C. Dielectric constant measurements were represented by a dielectric virial ex- pression. -
Theoretical Studies on As and Sb Sulfide Molecules
Mineral Spectroscopy: A Tribute to Roger G. Bums © The Geochemical Society, Special Publication No.5, 1996 Editors: M. D. Dyar, C. McCammon and M. W. Schaefer Theoretical studies on As and Sb sulfide molecules J. A. TOSSELL Department of Chemistry and Biochemistry University of Maryland, College Park, MD 20742, U.S.A. Abstract-Dimorphite (As4S3) and realgar and pararealgar (As4S4) occur as crystalline solids con- taining As4S3 and As4S4 molecules, respectively. Crystalline As2S3 (orpiment) has a layered structure composed of rings of AsS3 triangles, rather than one composed of discrete As4S6 molecules. When orpiment dissolves in concentrated sulfidic solutions the species produced, as characterized by IR and EXAFS, are mononuclear, e.g. ASS3H21, but solubility studies suggest trimeric species in some concentration regimes. Of the antimony sulfides only Sb2S3 (stibnite) has been characterized and its crystal structure does not contain Sb4S6 molecular units. We have used molecular quantum mechanical techniques to calculate the structures, stabilities, vibrational spectra and other properties of As S , 4 3 As4S4, As4S6, As4SIO, Sb4S3, Sb4S4, Sb4S6 and Sb4SlO (as well as S8 and P4S3, for comparison with previous calculations). The calculated structures and vibrational spectra are in good agreement with experiment (after scaling the vibrational frequencies by the standard correction factor of 0.893 for polarized split valence Hartree-Fock self-consistent-field calculations). The calculated geometry of the As4S. isomer recently characterized in pararealgar crystals also agrees well with experiment and is calculated to be about 2.9 kcal/mole less stable than the As4S4 isomer found in realgar. The calculated heats of formation of the arsenic sulfide gas-phase molecules, compared to the elemental cluster molecules As., Sb, and S8, are smaller than the experimental heats of formation for the solid arsenic sulfides, but shown the same trend with oxidation state. -
The Development of the Periodic Table and Its Consequences Citation: J
Firenze University Press www.fupress.com/substantia The Development of the Periodic Table and its Consequences Citation: J. Emsley (2019) The Devel- opment of the Periodic Table and its Consequences. Substantia 3(2) Suppl. 5: 15-27. doi: 10.13128/Substantia-297 John Emsley Copyright: © 2019 J. Emsley. This is Alameda Lodge, 23a Alameda Road, Ampthill, MK45 2LA, UK an open access, peer-reviewed article E-mail: [email protected] published by Firenze University Press (http://www.fupress.com/substantia) and distributed under the terms of the Abstract. Chemistry is fortunate among the sciences in having an icon that is instant- Creative Commons Attribution License, ly recognisable around the world: the periodic table. The United Nations has deemed which permits unrestricted use, distri- 2019 to be the International Year of the Periodic Table, in commemoration of the 150th bution, and reproduction in any medi- anniversary of the first paper in which it appeared. That had been written by a Russian um, provided the original author and chemist, Dmitri Mendeleev, and was published in May 1869. Since then, there have source are credited. been many versions of the table, but one format has come to be the most widely used Data Availability Statement: All rel- and is to be seen everywhere. The route to this preferred form of the table makes an evant data are within the paper and its interesting story. Supporting Information files. Keywords. Periodic table, Mendeleev, Newlands, Deming, Seaborg. Competing Interests: The Author(s) declare(s) no conflict of interest. INTRODUCTION There are hundreds of periodic tables but the one that is widely repro- duced has the approval of the International Union of Pure and Applied Chemistry (IUPAC) and is shown in Fig.1. -
Principles and Methods for the Risk Assessment of Chemicals in Food
WORLD HEALTH ORGANIZATION ORGANISATION MONDIALE DE LA SANTE EHC240: Principles and Methods for the Risk Assessment of Chemicals in Food SUBCHAPTER 4.5. Genotoxicity Draft 12/12/2019 Deadline for comments 31/01/2020 The contents of this restricted document may not be divulged to persons other than those to whom it has been originally addressed. It may not be further distributed nor reproduced in any manner and should not be referenced in bibliographical matter or cited. Le contenu du présent document à distribution restreinte ne doit pas être divulgué à des personnes autres que celles à qui il était initialement destiné. Il ne saurait faire l’objet d’une redistribution ou d’une reproduction quelconque et ne doit pas figurer dans une bibliographie ou être cité. Hazard Identification and Characterization 4.5 Genotoxicity ................................................................................. 3 4.5.1 Introduction ........................................................................ 3 4.5.1.1 Risk Analysis Context and Problem Formulation .. 5 4.5.2 Tests for genetic toxicity ............................................... 14 4.5.2.2 Bacterial mutagenicity ............................................. 18 4.5.2.2 In vitro mammalian cell mutagenicity .................... 18 4.5.2.3 In vivo mammalian cell mutagenicity ..................... 20 4.5.2.4 In vitro chromosomal damage assays .................. 22 4.5.2.5 In vivo chromosomal damage assays ................... 23 4.5.2.6 In vitro DNA damage/repair assays ....................... 24 4.5.2.7 In vivo DNA damage/repair assays ....................... 25 4.5.3 Interpretation of test results ......................................... 26 4.5.3.1 Identification of relevant studies............................. 27 4.5.3.2 Presentation and categorization of results ........... 30 4.5.3.3 Weighting and integration of results ..................... -
Arsinothricin, an Arsenic-Containing Non-Proteinogenic Amino Acid Analog of Glutamate, Is a Broad-Spectrum Antibiotic
ARTICLE https://doi.org/10.1038/s42003-019-0365-y OPEN Arsinothricin, an arsenic-containing non-proteinogenic amino acid analog of glutamate, is a broad-spectrum antibiotic Venkadesh Sarkarai Nadar1,7, Jian Chen1,7, Dharmendra S. Dheeman 1,6,7, Adriana Emilce Galván1,2, 1234567890():,; Kunie Yoshinaga-Sakurai1, Palani Kandavelu3, Banumathi Sankaran4, Masato Kuramata5, Satoru Ishikawa5, Barry P. Rosen1 & Masafumi Yoshinaga1 The emergence and spread of antimicrobial resistance highlights the urgent need for new antibiotics. Organoarsenicals have been used as antimicrobials since Paul Ehrlich’s salvarsan. Recently a soil bacterium was shown to produce the organoarsenical arsinothricin. We demonstrate that arsinothricin, a non-proteinogenic analog of glutamate that inhibits gluta- mine synthetase, is an effective broad-spectrum antibiotic against both Gram-positive and Gram-negative bacteria, suggesting that bacteria have evolved the ability to utilize the per- vasive environmental toxic metalloid arsenic to produce a potent antimicrobial. With every new antibiotic, resistance inevitably arises. The arsN1 gene, widely distributed in bacterial arsenic resistance (ars) operons, selectively confers resistance to arsinothricin by acetylation of the α-amino group. Crystal structures of ArsN1 N-acetyltransferase, with or without arsinothricin, shed light on the mechanism of its substrate selectivity. These findings have the potential for development of a new class of organoarsenical antimicrobials and ArsN1 inhibitors. 1 Department of Cellular Biology and Pharmacology, Florida International University, Herbert Wertheim College of Medicine, Miami, FL 33199, USA. 2 Planta Piloto de Procesos Industriales Microbiológicos (PROIMI-CONICET), Tucumán T4001MVB, Argentina. 3 SER-CAT and Department of Biochemistry and Molecular Biology, University of Georgia, Athens, GA 30602, USA. -
Indicators Versus Electrodes
Indicators versus Electrodes Titrant Indicator for visual endpoint Sample information Electrode Combined pH electrode for Acetic acid All indicators - aqueous solution Sample contains silver salt or Ferric ammonium sulfate TS silver nitrate VS is added in Combined silver electrode Ammonium thiocyanate excess for residual titration Ferric ammonium sulfate TS Sample contains mercury Combined gold electrode Other indicators Combined silver electrode Copper ion-selective electrode Barium Perchlorate All indicators and Ag/AgCl reference electrode Surfactant electrode resistant to Methylene blue Chlorinated solvents are used chlorinated solvents and Ag/AgCl reference electrode Benzethonium Chloride Surfactant electrode suitable for Other indicators non-ionic surfactants and Ag/AgCl reference electrode Copper ion-selective electrode Bismuth Nitrate All indicators and Ag/AgCl reference electrode Bromine All indicators Combined platinum electrode Ceric Ammonium Nitrate All indicators Combined platinum electrode Ceric Ammonium Sulfate All indicators Combined platinum electrode Ceric Sulfate All indicators Combined platinum electrode Copper ion-selective electrode Cupric Nitrate All indicators and Ag/AgCl reference electrode Polarizable gold or platinum Dichlorophenol–Indophenol All indicators electrode Hydroxy naphthol blue, calconcarboxylic acid Combined calcium ion-selective triturate, or combined calcium ion-selective electrode electrode Edetate Disodium Copper ion-selective electrode Other potentiometric indication and Ag/AgCl reference electrode -
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. -
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.