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Restricted Use Product Summary Report
Page 1 of 17 Restricted Use Product Summary Report (January 19, 2016) Percent Active Registration # Name Company # Company Name Active Ingredient(s) Ingredient 4‐152 BONIDE ORCHARD MOUSE BAIT 4 BONIDE PRODUCTS, INC. 2 Zinc phosphide (Zn3P2) 70‐223 RIGO EXOTHERM TERMIL 70 VALUE GARDENS SUPPLY, LLC 20 Chlorothalonil 100‐497 AATREX 4L HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 42.6 Atrazine 100‐585 AATREX NINE‐O HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 88.2 Atrazine 100‐669 CURACRON 8E INSECTICIDE‐MITICIDE 100 SYNGENTA CROP PROTECTION, LLC 73 Profenofos 100‐817 BICEP II MAGNUM HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 33; 26.1 Atrazine; S‐Metolachlor 100‐827 BICEP LITE II MAGNUM HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 28.1; 35.8 Atrazine; S‐Metolachlor 100‐886 BICEP MAGNUM 100 SYNGENTA CROP PROTECTION, LLC 33.7; 26.1 Atrazine; S‐Metolachlor 100‐898 AGRI‐MEK 0.15 EC MITICIDE/INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 2 Abamectin 100‐903 DENIM INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 2.15 Emamectin benzoate 100‐904 PROCLAIM INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 5 Emamectin benzoate 100‐998 KARATE 1EC 100 SYNGENTA CROP PROTECTION, LLC 13.1 lambda‐Cyhalothrin 100‐1075 FORCE 3G INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 3 Tefluthrin Acetochlor; Carbamothioic acid, dipropyl‐ 100‐1083 DOUBLEPLAY SELECTIVE HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 16.9; 67.8 , S‐ethyl ester 100‐1086 KARATE EC‐W INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 13.1 lambda‐Cyhalothrin 100‐1088 SCIMITAR GC INSECTICIDE 100 SYNGENTA CROP PROTECTION, -
"U/^ ((*.U \ BIBLIOTHEEK STARINGGEBOUW Volatilization of Tri-Allate, Ethoprophos and Parathion Measured with Four Methods After Spraying on a Sandy Soil
"u/^ ((*.u \ BIBLIOTHEEK STARINGGEBOUW Volatilization of tri-allate, ethoprophos and parathion measured with four methods after spraying on a sandy soil G. Bor F. van den Berg J.H. Smelt R.A. Smidt A.E. van de Peppel-Groen M. Leistra Report 104 DLO Winand Staring Centre, Wageningen (The Netherlands), 1995 1 h FEB. 1998 0000' ABSTRACT Bor, G., F. van den Berg, J.H. Smelt, R.A. Smidt, A.E. van de Peppel-Groen, M. Leistra, 1995. Volatilization of tri-allate, ethoprophos and parathion measured withfour methods after spraying on a sandy soil. Wageningen (The Netherlands), DLO Winand Staring Centre. Report 104. 62 pp.; 9 Figs; 6 Tables; 14 Refs; 3 Annex. At about eleven times after application of tri-allate, ethoprophos and parathion to a sandy soil, their rates of volatilization were determined with the aerodynamic method (AD),th e Bowen-ratio method (BR), the theoretical-profile method (TP) and the Box method (B). The volatilization was highest for tri-allate and lowest for parathion. On the first day after application, the volatilization rate decreased sharply,bu tthereafte r the decreasewa smor egradual .Th edifference s involatilizatio n rate asdetermine d withth eAD ,B R andT Pmethod s werecomparativel y small.Th erate sdetermine d with the Box method were mostly lower than those determined with the other methods. Keywords: aerodynamic method, air quality, air sampling, Bowen ratio method, Box method, field experiment, gas chromatography, pesticide, polystyrene, theoretical-profile method, XAD ISSN 0927-4537 ©1995 DLO Winand Staring Centre for Integrated Land, Soil and Water Research (SC-DLO) P.O. -
Holocene Environmental Changes Disclosed from Anoxic Fjord Sediments by Biomarkers and Their Radiocarbon Content
GEOLOGICA ULTRAIECTINA Mededelingen van de Faculteit Geowetenschappen Universiteit Utrecht No. 227 Holocene environmental changes disclosed from anoxic fjord sediments by biomarkers and their radiocarbon content Rienk H. Smittenberg Holocene environmental changes disclosed from anoxic fjord sediments by biomarkers and their radiocarbon content Holocene milieuveranderingen gereconstrueerd uit anoxische fjord sedimenten middels biomarkers en hun radio-aktief koolstof gehalte (met een samenvatting in het Nederlands) Proefschrift ter verkrijging van de graad van doctor aan de Universiteit Utrecht op gezag van de Rector Magnificus, Prof. Dr. W.H. Gispen, ingevolge het besluit van het College voor Promoties in het openbaar te verdedigen op maandag 15 september 2003 des middags te 4.15 uur door Rienk Hajo Smittenberg geboren op 23 maart 1973 te Eck en Wiel Promotor: Prof. Dr. J.W. de Leeuw Department of Geochemistry Utrecht University Utrecht, The Netherlands Copromotores: Dr. Ir. J.S. Sinninghe Damsté Department of Geochemistry Utrecht University Utrecht, The Netherlands Dr. S. Schouten Department of Marine Biogeochemistry and Toxicology Royal Netherlands Institute of Sea Research Texel, The Netherlands The research described in this thesis was carried out at the Department of Biogeochemistry and Toxicology of the Royal Netherlands Institute of Sea Research, P.O. Box 59, 1790 AB Den Burg, The Netherlands. The investigations were supported by the Research Council for Earth and Life Science (ALW) with the financial support from the Netherlands -
Application of Biomarker Compounds As Tracers for Sources and Fates of Natural and Anthropogenic Organic Matter in Tile Environment
AN ABSTRACT OF THE DISSERTATION OF Daniel R. Oros for the degree of Doctor of Philosophy in Environmental Sciences presented on September 24. 1999. Title: Application of Biomarker Compoundsas Tracers for Sources and Fates of Natural and Anthropogenic Organic Matter in the Environment. Redacted for Privacy Abstract approved: Bernd R.T. Simoneit Determination of the source and fate of natural (higher plant lipids, marine lipids, etc.) and anthropogenically (e.g., petroleum, coal emissions) derived hydrocarbons and oxygenated compounds in the environment was accomplished using gas chromatography (GC) and gas chromatography-mass spectrometry (GC- MS) to characterize or identify molecular biomarkers to be utilized as tracers. The distributions and abundances of biomarkers such as straight chain homologous series (e.g., n-alkanes, n-alkanoic acids, n-alkan-2-ones, n-alkanols, etc.) and cyclic terpenoid compounds (e.g., sesquiterpenoids, diterpenoids, steroids, triterpenoids) were identified in epicuticular waxes from conifers of western North America (natural emissions). These biomarkers and their thermal alteration derivativeswere also identified in smoke emissions from known vegetation sources (e.g., conifers, deciduous trees and grasses) and were then applied as tracers in soils, soils that contained wildfire residues and soillriver mud washout after wildfire burning. Where possible, the reaction pathways of transformation from the parentprecursor compounds to intermediate and final alteration products were determined from GC- MS data. In addition, molecular tracer analysis was applied to air, water and sediment samples collected from a lacustrine setting (Crater Lake, OR) in order to determine the identities, levels and fates of anthropogenic (i.e., petroleum hydrocarbon contamination from boating and related activities) hydrocarbons ina pristine organic matter sink. -
H4R Position on Rosin As One Substance For
H4R Position Statement on Rosin, Rosin Salts and Rosin Esters Registered as One Substance 7th February 2019 REACH registrations of Rosin, Rosin Salts and Rosin Esters H4R Position Statement on One Substance Registration Historically, various names, CAS, and EINECS numbers have existed for rosin. REACH1 mandates “One Substance – One Registration”. This obliged the Rosin registrants to carefully examine the composition of their substances of interest. They concluded that, although Rosin is historically listed under different names and EINECS and CASRNs (e.g. Rosin; Tall-oil rosin; Resin acids and rosin acids; etc.), it needed to be considered as one and the same substance. In addition, the registrants concluded that rosin is a chemical substance of Unknown or Variable Composition, Complex Reaction Products and Biological Materials (UVCB). In other words, rosin was listed on EINECS and CAS under different names, but the rosin registrants determined that differentiation was not justified and appropriate as these are the same UVCB substances. Therefore, Rosin with CAS 8050-09-7 was chosen. Appendix 1 to this document outlines the registrations that cover each of these substances. This decision and its rationale for one rosin registration is well documented in two papers: “Justification for grouping rosin and rosin derivatives into families” by Gary McCallister (Hercules), Bert Lenselink (Hexion), Jerrold Miller (Arizona Chemical), Bill Grady (Arizona Chemical) and Leon Rodenburg (Eastman Chemical), 24 August 20102 “Justification for considering Rosin as a Single Substance” by H4R Consortium, 22 February 20103 Based on these papers, it was concluded that, for rosin and the derived rosin salts, fortified rosin, fortified rosin salts, rosin esters and fortified rosin esters, the starting rosin is not relevant. -
40 CFR Ch. I (7–1–18 Edition) § 455.61
§ 455.61 40 CFR Ch. I (7–1–18 Edition) from: the operation of employee show- § 455.64 Effluent limitations guidelines ers and laundry facilities; the testing representing the degree of effluent of fire protection equipment; the test- reduction attainable by the applica- ing and emergency operation of safety tion of the best available tech- showers and eye washes; or storm nology economically achievable water. (BAT). (d) The provisions of this subpart do Except as provided in 40 CFR 125.30 not apply to wastewater discharges through 125.32, any existing point from the repackaging of microorga- source subject to this subpart must nisms or Group 1 Mixtures, as defined achieve effluent limitations rep- under § 455.10, or non-agricultural pes- resenting the degree of effluent reduc- ticide products. tion attainable by the application of the best available technology economi- § 455.61 Special definitions. cally achievable: There shall be no dis- Process wastewater, for this subpart, charge of process wastewater pollut- means all wastewater except for sani- ants. tary water and those wastewaters ex- § 455.65 New source performance cluded from the applicability of the standards (NSPS). rule in § 455.60. Any new source subject to this sub- § 455.62 Effluent limitations guidelines part which discharges process waste- representing the degree of effluent water pollutants must meet the fol- reduction attainable by the applica- lowing standards: There shall be no dis- tion of the best practicable pollut- charge of process wastewater pollut- ant control technology (BPT). ants. Except as provided in 40 CFR 125.30 through 125.32, any existing point § 455.66 Pretreatment standards for existing sources (PSES). -
Reduction of Nitroaromatic Pesticides with Zero-Valent Iron
Chemosphere 54 (2004) 255–263 www.elsevier.com/locate/chemosphere Reduction of nitroaromatic pesticides with zero-valent iron Young-Soo Keum, Qing X. Li * Department of Molecular Biosciences and Bioengineering, University of Hawaii, 1955 East-West Road, Ag Sci 218, Honolulu, HI 96822, USA Received 5 February 2003; received in revised form 4 June 2003; accepted 4 August 2003 Abstract Reduction of eleven nitroaromatic pesticides was studied with zero-valent iron powder. Average half-lives ranged from 2.8 to 6.3 h and the parent compounds were completely reduced after 48–96 h. The di-nitro groups of the 2,6- dinitroaniline herbicides were rapidly reduced to the corresponding diamines, with a negligible amount of partially reduced monoamino or nitroso products. Low levels of de-alkylated products were observed after 10 days. The nitro group of the organophosphorus insecticides was reduced dominantly to the monoamines but in a slower rate than the 2,6-dinitroanilines. A trace amount of oxon products was found. Reduction of nitro to amino was also the predominant reaction for the diphenyl ether herbicides. Aromatic de-chlorination and de-alkylation were minor reactions. These amine products were more stable than the parent compounds and 60% or more of the amines were detected after two weeks. Humic acid decreased the reduction rates of pendimethalin, and dichlone (a known quinone redox mediator) counteracted the effect of humic acid on the reactivity. Storage of iron powder under air decreased the reactivity very rapidly due to iron oxidation. Repeated use of iron powder also showed similar results. The reduced activity of air- oxidized iron was recovered by purging with hydrogen, but not nitrogen. -
8341 No Clean Flux Paste
8341 No Clean Flux Paste MG Chemicals UK Limited Version No: A-1.0 2 Issue Date:26/04/2018 Safety Data Sheet (Conforms to Regulation (EU) No 2015/830) Revision Date: 14/01/2021 L.REACH.GBR.EN SECTION 1 IDENTIFICATION OF THE SUBSTANCE / MIXTURE AND OF THE COMPANY / UNDERTAKING 1.1. Product Identifier Product name 8341 Synonyms SDS Code: 8341; 8341-10ML; 8341-10MLCA, 8341B-10ML | UFI: HGH0-205D-2003-EPAT Other means of identification No Clean Flux Paste 1.2. Relevant identified uses of the substance or mixture and uses advised against Relevant identified uses For use with leaded and unleaded solder during soldering process Uses advised against Not Applicable 1.3. Details of the supplier of the safety data sheet Registered company name MG Chemicals UK Limited MG Chemicals (Head office) Heame House, 23 Bilston Street, Sedgely Dudley DY3 1JA United Address 9347 - 193 Street Surrey V4N 4E7 British Columbia Canada Kingdom Telephone +(44) 1663 362888 +(1) 800-201-8822 Fax Not Available +(1) 800-708-9888 Website Not Available www.mgchemicals.com Email [email protected] [email protected] 1.4. Emergency telephone number Association / Organisation Verisk 3E (Access code: 335388) Not Available Emergency telephone numbers +(44) 20 35147487 Not Available Other emergency telephone +(0) 800 680 0425 Not Available numbers SECTION 2 HAZARDS IDENTIFICATION 2.1. Classification of the substance or mixture Classification according to regulation (EC) No 1272/2008 H319 - Eye Irritation Category 2, H317 - Skin Sensitizer Category 1, H334 - Respiratory Sensitizer Category 1 [CLP] [1] 1. Classified by Chemwatch; 2. Classification drawn from EC Directive 67/548/EEC - Annex I ; 3. -
Polycyclic Aromatic Hydrocarbon Structure Index
NIST Special Publication 922 Polycyclic Aromatic Hydrocarbon Structure Index Lane C. Sander and Stephen A. Wise Chemical Science and Technology Laboratory National Institute of Standards and Technology Gaithersburg, MD 20899-0001 December 1997 revised August 2020 U.S. Department of Commerce William M. Daley, Secretary Technology Administration Gary R. Bachula, Acting Under Secretary for Technology National Institute of Standards and Technology Raymond G. Kammer, Director Polycyclic Aromatic Hydrocarbon Structure Index Lane C. Sander and Stephen A. Wise Chemical Science and Technology Laboratory National Institute of Standards and Technology Gaithersburg, MD 20899 This tabulation is presented as an aid in the identification of the chemical structures of polycyclic aromatic hydrocarbons (PAHs). The Structure Index consists of two parts: (1) a cross index of named PAHs listed in alphabetical order, and (2) chemical structures including ring numbering, name(s), Chemical Abstract Service (CAS) Registry numbers, chemical formulas, molecular weights, and length-to-breadth ratios (L/B) and shape descriptors of PAHs listed in order of increasing molecular weight. Where possible, synonyms (including those employing alternate and/or obsolete naming conventions) have been included. Synonyms used in the Structure Index were compiled from a variety of sources including “Polynuclear Aromatic Hydrocarbons Nomenclature Guide,” by Loening, et al. [1], “Analytical Chemistry of Polycyclic Aromatic Compounds,” by Lee et al. [2], “Calculated Molecular Properties of Polycyclic Aromatic Hydrocarbons,” by Hites and Simonsick [3], “Handbook of Polycyclic Hydrocarbons,” by J. R. Dias [4], “The Ring Index,” by Patterson and Capell [5], “CAS 12th Collective Index,” [6] and “Aldrich Structure Index” [7]. In this publication the IUPAC preferred name is shown in large or bold type. -
INDEX to PESTICIDE TYPES and FAMILIES and PART 180 TOLERANCE INFORMATION of PESTICIDE CHEMICALS in FOOD and FEED COMMODITIES
US Environmental Protection Agency Office of Pesticide Programs INDEX to PESTICIDE TYPES and FAMILIES and PART 180 TOLERANCE INFORMATION of PESTICIDE CHEMICALS in FOOD and FEED COMMODITIES Note: Pesticide tolerance information is updated in the Code of Federal Regulations on a weekly basis. EPA plans to update these indexes biannually. These indexes are current as of the date indicated in the pdf file. For the latest information on pesticide tolerances, please check the electronic Code of Federal Regulations (eCFR) at http://www.access.gpo.gov/nara/cfr/waisidx_07/40cfrv23_07.html 1 40 CFR Type Family Common name CAS Number PC code 180.163 Acaricide bridged diphenyl Dicofol (1,1-Bis(chlorophenyl)-2,2,2-trichloroethanol) 115-32-2 10501 180.198 Acaricide phosphonate Trichlorfon 52-68-6 57901 180.259 Acaricide sulfite ester Propargite 2312-35-8 97601 180.446 Acaricide tetrazine Clofentezine 74115-24-5 125501 180.448 Acaricide thiazolidine Hexythiazox 78587-05-0 128849 180.517 Acaricide phenylpyrazole Fipronil 120068-37-3 129121 180.566 Acaricide pyrazole Fenpyroximate 134098-61-6 129131 180.572 Acaricide carbazate Bifenazate 149877-41-8 586 180.593 Acaricide unclassified Etoxazole 153233-91-1 107091 180.599 Acaricide unclassified Acequinocyl 57960-19-7 6329 180.341 Acaricide, fungicide dinitrophenol Dinocap (2, 4-Dinitro-6-octylphenyl crotonate and 2,6-dinitro-4- 39300-45-3 36001 octylphenyl crotonate} 180.111 Acaricide, insecticide organophosphorus Malathion 121-75-5 57701 180.182 Acaricide, insecticide cyclodiene Endosulfan 115-29-7 79401 -
Phytotoxicity of Some Organophosphate Insecticides to Oughly with Air Dry, Sieved Soil, to Pro Duce Rates of 37.5, 75 and ISO Mg Aj
Plant Protection Quarterly VoI.7(1} 1992 23 -------------------------------- ties of each pesticide were shaken thor Phytotoxicity of some organophosphate insecticides to oughly with air dry, sieved soil, to pro duce rates of 37.5, 75 and ISO mg aj. L-' onions and carrots during germination and emergence soil. Each pot constituted one plot. If it is assumed that in a field situation, P.J. Sinclair, New South Wales Agriculture, Horticultural Research and band-in-furrow treatment would treat a Advisory Station, Griffith, New South Wales 2680, Australia. strip 50 mm wide by 20 mm deep, the rates tested would correspond to 37.5, 75 R.J. Neeson and P.A. Williams, New South Wales Agriculture, Agricultural and 150 mg a.i. m" row, or 0.5,1.0 and 2.0 institute, Yanco, New South Wales 2703, Australia. kg a.i. ha" at a row spacing of 75 cm. The low and medium rates are then compara Summary ble to ra tes used in the field by Getzin The phytotoxicity of some commonly phytotoxicity from carbofuran applied to (1973), Thompson et al. (1981) and used insecticides to onions (Allium cepa) onions as a seed dressing. Chlorpyrifos is Goodyer et al. (1989) . and carrots (Daucus carota) during es generally non-phytotoxic at recom Daily counts of emerged seedlings were tablishment was assessed in pot trials. mended rates and methods of application, made at 7 to 18 days and at 21 days after Terbufos, ethoprophos, phoxirn and but some crops are especially sensitive to first watering. These data were used to de carbofuran (all 10% a.L granular fonnu it during the seedling stage or if the termine the total number of seedlings lations) and chlorpyrifos (25% a.i. -
Synthesis of High Carbon Materials from Acetylenic Precursors
Reprinted from The Journal of Organic Chemistry, 1988, Vol. 53, page 2489 Copyright @ 1988 by the American Chemical Society and reprinted by permission of the copyright owner. Synthesis of High Carbon Materials from Acetylenic Precursors. Preparation of Aromatic Monomers Bearing Multiple Ethynyl Groups1 Thomas X. Neenan and George M. Whitesides* Department of Chemistry, Harvard University, Cambridge, Massachusetts 02138 Received October 13, 1987 The synthesis of polyethynyl aromatics as starting materials for the preparation of highly cross-linked organic solids containing high atom fractions of carbon is described. Treatment of bromo- and iodoaromatic compounds with (trimethylsily1)acetylene (TMSA) in the presence of palladium(0)and copper(1) in amine solvents yields (trimethylsily1)ethynyl-substituted aromatics. The TMS protecting groups can be removed by hydrolysis with mild base. Compounds prepared by using this technique include 1,3-diethynylbenzene,2,5-diethynylthiophene, 1,3-diethynyltetrafluorobenzene,1,4-diethynyltetrafluorobenzene, 2-ethynylthiazole, 2,4-diethynylthiazole, 2,7- diethynylnaphthalene, hexakis((trimethylsilyl)ethynyl)benzene, tetraethynylthiophene, 2,5-bis((trimethy1- silyl)ethynyl)-3,4-bis(3-hydroxy-3-methyl-l-butynyl)thiophene,2,5-diethyny1-3,4-bis(3-hydroxy-3-methyl-l-b~- tynyl)thiophene, 2,5-bis(4-(2-thienyl)butadiynyl)-3,4-bis(3-hydroxy-3-methyl-l-butynyl)thiophene,and 2,5-bis- (4-(2-thienyl)butadiynyl)-3,4-diethynylthiophene. Introduction We are engaged in a project aimed at the preparation of organic solids