Utilization of a New Toxicity Testing System As a Drinking Water
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Carbamate Pesticides Aldicarb Aldicarb Sulfoxide Aldicarb Sulfone
Connecticut General Statutes Sec 19a-29a requires the Commissioner of Public Health to annually publish a list setting forth all analytes and matrices for which certification for testing is required. Connecticut ELCP Drinking Water Analytes Revised 05/31/2018 Microbiology Total Coliforms Fecal Coliforms/ E. Coli Carbamate Pesticides Legionella Aldicarb Cryptosporidium Aldicarb Sulfoxide Giardia Aldicarb Sulfone Carbaryl Physicals Carbofuran Turbidity 3-Hydroxycarbofuran pH Methomyl Conductivity Oxamyl (Vydate) Minerals Chlorinated Herbicides Alkalinity, as CaCO3 2,4-D Bromide Dalapon Chloride Dicamba Chlorine, free residual Dinoseb Chlorine, total residual Endothall Fluoride Picloram Hardness, Calcium as Pentachlorophenol CaCO3 Hardness, Total as CaCO3 Silica Chlorinated Pesticides/PCB's Sulfate Aldrin Chlordane (Technical) Nutrients Dieldrin Endrin Ammonia Heptachlor Nitrate Heptachlor Epoxide Nitrite Lindane (gamma-BHC) o-Phosphate Metolachlor Total Phosphorus Methoxychlor PCB's (individual aroclors) Note 1 PCB's (as decachlorobiphenyl) Note 1 Demands Toxaphene TOC Nitrogen-Phosphorus Compounds Alachlor Metals Atrazine Aluminum Butachlor Antimony Diquat Arsenic Glyphosate Barium Metribuzin Beryllium Paraquat Boron Propachlor Cadmium Simazine Calcium Chromium Copper SVOC's Iron Benzo(a)pyrene Lead bis-(2-ethylhexyl)phthalate Magnesium bis-(ethylhexyl)adipate Manganese Hexachlorobenzene Mercury Hexachlorocyclopentadiene Molybdenum Nickel Potassium Miscellaneous Organics Selenium Dibromochloropropane (DBCP) Silver Ethylene Dibromide (EDB) -
"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. -
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. -
P-Listed Hazardous Wastes
P-Listed Hazardous Wastes The Environmental Protection Agency (EPA) has identified a number of chemicals on the EPA “P-list” that present an especially acute hazard when disposed of as hazardous waste. Because of their acute hazards, there are more stringent requirements when disposing of these wastes: ►Container size: When collecting p-listed chemicals as waste, the volume of the hazardous waste container must not exceed one quart (approximately one liter). ►Empty containers: Empty containers that held p-listed chemicals must also be disposed of as hazardous waste. They are not allowed to be washed or re-used. ►Contaminated materials: Disposable materials that become contaminated with p-listed chemicals (e.g. gloves, weighing boats, etc.) must also be disposed of as hazardous waste. Non-disposable materials must be “triple-rinsed”, or rinsed three times to remove the contamination. This rinsate must be collected as hazardous waste. Materials contaminated with p-listed chemicals may not be washed or re-used until they have been triple-rinsed. Remember: - Label the waste as hazardous waste. Most common p-listed wastes Just like all other hazardous wastes, p-listed Chemical CAS number wastes must be labeled with the words Acrolein 107–02–8 “hazardous waste”, the complete chemical Allyl alcohol 107–18–6 name, and the associated hazard Arsenic compounds Varies characteristics (e.g., ignitable, corrosive, Inorganic cyanide Varies toxic, or reactive). salts Carbon disulfide 75-15-0 - Use disposable materials whenever Cyanogen and 460-19-5, 506-77-4 possible. Triple-rising non-disposable Cyanogen Chloride material generates a lot of waste, which can 2,4-Dinitrophenol 51–28–5 be difficult to dispose of safely. -
Determination of Organophosphorus Pesticide Residues in Vegetables Using Solid Phase Micro-Extraction Coupled with Gas Chromatography–flame Photometric Detector
Arabian Journal of Chemistry (2015) xxx, xxx–xxx King Saud University Arabian Journal of Chemistry www.ksu.edu.sa www.sciencedirect.com ORIGINAL ARTICLE Determination of organophosphorus pesticide residues in vegetables using solid phase micro-extraction coupled with gas chromatography–flame photometric detector Haizarul Aida Sapahin, Ahmad Makahleh *, Bahruddin Saad * School of Chemical Sciences, Universiti Sains Malaysia, 11800 Minden, Penang, Malaysia Received 17 July 2014; accepted 9 December 2014 KEYWORDS Abstract An adequate and simple analytical method based on solid-phase microextraction Organophosphorus pesticide; (SPME) followed by gas chromatography–flame photometric detection (GC–FPD) for the determi- Direct immersed-solid phase nation of eleven organophosphorus pesticide residues (i.e., ethoprophos, sulfotep, diazinon, tolclo- microextraction; fos-methyl, fenitrothion, chlorpyrifos, isofenphos, methidathion, ethion, triazophos, leptophos) in Gas chromatography–flame vegetables samples (cabbage, kale and mustard) was developed. Important parameters that influ- photometric detector; ence the extraction efficiency (i.e., fibre type, extraction modes, extraction time, salt addition, Vegetables desorption time and temperature) were systematically investigated. Four types of commercially available fibres (i.e., 50/30 lm divinylbenzene/carboxen/polydimethylsiloxane (DVB/CAR/PDMS), 65 lm polydimethylsiloxane/divinylbenzene (PDMS/DVB), 100 lm polydimethylsiloxane (PDMS), and 85 lm polyacrylate (PA)) were evaluated. PA fibre exhibited the best performance and was used for the rest of the studies. The optimised extraction conditions were: extraction time, 30 min at room temperature; stirring speed, 1275 rpm; salt content, 10% NaCl; desorption time and temper- ature, 11 min at 260 °C; and no pH adjustment of the sample extract. The method was validated over the range 0.1–100 lg/L. -
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. -
The List of Extremely Hazardous Substances)
APPENDIX A (THE LIST OF EXTREMELY HAZARDOUS SUBSTANCES) THRESHOLD REPORTABLE INVENTORY RELEASE QUANTITY QUANTITY CAS NUMBER CHEMICAL NAME (POUNDS) (POUNDS) 75-86-5 ACETONE CYANOHYDRIN 500 10 1752-30-3 ACETONE THIOSEMICARBAZIDE 500/500 1,000 107-02-8 ACROLEIN 500 1 79-06-1 ACRYLAMIDE 500/500 5,000 107-13-1 ACRYLONITRILE 500 100 814-68-6 ACRYLYL CHLORIDE 100 100 111-69-3 ADIPONITRILE 500 1,000 116-06-3 ALDICARB 100/500 1 309-00-2 ALDRIN 500/500 1 107-18-6 ALLYL ALCOHOL 500 100 107-11-9 ALLYLAMINE 500 500 20859-73-8 ALUMINUM PHOSPHIDE 500 100 54-62-6 AMINOPTERIN 500/500 500 78-53-5 AMITON 500 500 3734-97-2 AMITON OXALATE 100/500 100 7664-41-7 AMMONIA 500 100 300-62-9 AMPHETAMINE 500 1,000 62-53-3 ANILINE 500 5,000 88-05-1 ANILINE,2,4,6-TRIMETHYL- 500 500 7783-70-2 ANTIMONY PENTAFLUORIDE 500 500 1397-94-0 ANTIMYCIN A 500/500 1,000 86-88-4 ANTU 500/500 100 1303-28-2 ARSENIC PENTOXIDE 100/500 1 THRESHOLD REPORTABLE INVENTORY RELEASE QUANTITY QUANTITY CAS NUMBER CHEMICAL NAME (POUNDS) (POUNDS) 1327-53-3 ARSENOUS OXIDE 100/500 1 7784-34-1 ARSENOUS TRICHLORIDE 500 1 7784-42-1 ARSINE 100 100 2642-71-9 AZINPHOS-ETHYL 100/500 100 86-50-0 AZINPHOS-METHYL 10/500 1 98-87-3 BENZAL CHLORIDE 500 5,000 98-16-8 BENZENAMINE, 3-(TRIFLUOROMETHYL)- 500 500 100-14-1 BENZENE, 1-(CHLOROMETHYL)-4-NITRO- 500/500 500 98-05-5 BENZENEARSONIC ACID 10/500 10 3615-21-2 BENZIMIDAZOLE, 4,5-DICHLORO-2-(TRI- 500/500 500 FLUOROMETHYL)- 98-07-7 BENZOTRICHLORIDE 100 10 100-44-7 BENZYL CHLORIDE 500 100 140-29-4 BENZYL CYANIDE 500 500 15271-41-7 BICYCLO[2.2.1]HEPTANE-2-CARBONITRILE,5- -
Application of Dried Blood Spots for the Determination of Organophosphorus Pesticides by GC-MS/MS
UNIVERSIDADE DA BEIRA INTERIOR Ciências Application of dried blood spots for the determination of organophosphorus pesticides by GC-MS/MS Sofia Pires Seixo Soares Dissertação para obtenção do Grau de Mestre em Bioquímica (2º ciclo de estudos) Orientador: Doutor Mário Jorge Dinis Barroso Co-orientador: Professora Doutora Maria Eugenia Gallardo Alba Covilhã, junho de 2018 Agradecimentos A realização de uma dissertação de mestrado é o culminar de muitas horas de estudo, reflexão e trabalho pessoal, mas representa também uma etapa que não seria possível sem o contributo fundamental de várias pessoas. À Doutora Eugénia Gallardo e ao Doutor Mário Barroso, como excelentes mentores que são, quero agradecer toda a orientação, motivação, incentivo e confiança. Toda a ajuda e partilha de experiência e conhecimento durante todo este percurso. Ao Tiago Rosado, pela imprescindível ajuda e disponibilidade constante, bem como pela amizade. À Joana Gonçalves e ao Ângelo Luís um agradecimento especial pela amizade e carinho demonstrado ao longo deste ano. A todos, quero agradecer pelo bom ambiente proporcionado. Aos meus pais Ana Soares e José Soares, a quem dedico este feito, por me darem a possibilidade de concretizar conquistas como esta, pelo apoio incondicional, por sempre terem acreditado em mim e por fazerem parte deste momento. Aos meus avós e restante família, por todo o apoio e preocupação. Um agradecimento particular à Inês Ramos, à Rita Marques, à Maria Cunha e ao Pedro Batista pelo companheirismo, amizade e apoio de há tantos anos. E por último, mas nunca menos importante, um enorme obrigada ao meu namorado António Fernandes por toda a paciência, pelo incansável apoio, carinho e ajuda. -
USGS.Comments. Insec.Pdf
ABBREVIATIONS USED – Insecticides – (data source: U.S. Geological Survey) WELL AND SAMPLE IDENTIFIERS LOCAL – Local number used to identify well. First two letters represent the county (AD = Adams County), the following digits represent incremental numbers. STAID – Station identifier. For the U.S. Geological Survey wells, it is 15 digits long and is comprised of the latitude and longitude plus a two digit sequence number. SOURCE – U.S. Geological Survey (USGS). Samples collected for a wide range of water- quality, water resources, and other hydrogeologic investigations. DATES – Date the sample was collected. LAT – Latitude of well, in degrees, minutes, and seconds in format DDMMSS. LONG – Longitude of well, in degrees, minutes, and seconds in format DDMMSS. CNTYC – County where well is located. For USGS the counties are Adams, Allegheny, Armstrong, Bedford, Berks, Blair, Bradford, Bucks, Butler, Cambria, Carbon, Centre, Chester, Clarion, Clearfield, Clinton, Columbia, Crawford, Cumberland, Dauphin, Erie, Fayette, Franklin, Fulton, Greene, Huntingdon, Indiana, Jefferson, Juniata, Lancaster, Lebanon, Lehigh, Lycoming, McKean, Mifflin, Monroe, Montgomery, Northampton, Northumberland, Perry, Pike, Schuylkill, Snyder, Somerset, Tioga, Warren, Washington, Wayne, Westmoreland, York. BASINS – The PADEP basin (numbers range from 1-35) the well is located in. For USGS, wells are located in Basins 1, 4, 5, 6, 10, 11, 12, 13, 14, 15, 16, 17, 18, 19, 20, 21, 22, 23, 24, 25, 26, 27, 28, 29, 31, 32, 33, 34, 35. GEO1 – General geologic (bedrock) unit. For Fixed Station Network, the bedrock units are bcoal (bituminous coal bearing), dkcrys (dark crystalline), ltcrys (light crystalline), pocarb (Precambrian through Ordovician carbonates), qscong (quartz, sandstone, and conglomerate), redsed (red sedimentary rocks), schist (schist), sdcarb (Silurian and Devonian carbonates), shale (shale), trised (Triassic age sedimentary rocks). -
Agricultural Chemical Usage Restricted Use Summary Agricultural Statistics Board October 2000 1 NASS, USDA Highlights
United States Department of Agriculture Agricultural Chemical National Agricultural Statistics Usage Service 1999 Restricted Use Summary Ag Ch 1 (00) a October 2000 Update Alert The herbicide trifluralin was erroneously listed in the corn, upland cotton, peanuts, fall potatoes, soybeans and sunflower tables (pages 3-7). Trifluralin is not restricted for use on those crops. In addition, summary errors for the chemicals ethyl parathion and methyl parathion were discovered for sunflowers in Kansas. Previously published applications of the insecticide ethyl parathion on sunflowers in Kansas were in error and should have all been reported as applications of methyl parathion. The affected sunflower table has been revised (page 7). 1999 Agricultural Chemical Use Estimates for Restricted Use Pesticides Overview: As determined by the U.S. Environmental Protection Agency (EPA), a restricted use pesticide is a pesticide which is available for purchase and use only by certified pesticide applicators or persons under their direct supervision and only for the uses covered by the certified applicator’s certification. This group of pesticides is not available for use by the general public because of the very high toxicities and /or environmental hazards associated with these active ingredients. An active ingredient may be restricted for one crop but not for another. This report shows only those active ingredients which are restricted for each specific crop, based on the “Restricted Use Product (RUP) Report, June 2000" published by the EPA. The agricultural chemical use estimates in this report are based on data compiled from the Agricultural Resource Management Study, the Fruit Chemical Use Survey, and the 1999 Fall Area Survey. -
Surface-Water Quality, Oneida Reservation and Vicinity, Wisconsin, 1997-98
U.S. Department of the Interior U.S. Geological Survey Surface-Water Quality, Oneida Reservation and Vicinity, Wisconsin, 1997-98 Water-Resources Investigations Report 00-4179 Prepared in cooperation with the Oneida Tribe of Indians of Wisconsin science for a changing world Surface-Water Quality, Oneida Reservation and Vicinity, Wisconsin, 1997-98 By Morgan A. Schmidt, Kevin D. Richards, and Barbara C. Scudder U.S. GEOLOGICAL SURVEY Water-Resources Investigations Report 00-4179 Prepared in cooperation with the Oneida Tribe of Indians of Wisconsin Middleton, Wisconsin 2000 ruses science for a changing world U.S. DEPARTMENT OF THE INTERIOR BRUCE BABBITT, Secretary U.S. GEOLOGICAL SURVEY Charles G. Groat, Director Any use of trade, product, or firm names is for descriptive purposes only and does not imply endorsement by the U.S. Government. For additional information write to: Copies of this report can be purchased from: District Chief U.S. Geological Survey U.S. Geological Survey Branch of Information Services 8505 Research Way Box 25286 Middleton, Wl 53562-3586 Denver, CO 80225-0286 CONTENTS Abstract ............................................................... 1 Introduction............................................................................................._^ 2 Description of Oneida Reservation study area............................................................................................................ 2 Factors affecting surface-water quality...................................................................................................................... -
Environmental Health Criteria 63 ORGANOPHOSPHORUS
Environmental Health Criteria 63 ORGANOPHOSPHORUS INSECTICIDES: A GENERAL INTRODUCTION Please note that the layout and pagination of this web version are not identical with the printed version. Organophophorus insecticides: a general introduction (EHC 63, 1986) INTERNATIONAL PROGRAMME ON CHEMICAL SAFETY ENVIRONMENTAL HEALTH CRITERIA 63 ORGANOPHOSPHORUS INSECTICIDES: A GENERAL INTRODUCTION This report contains the collective views of an international group of experts and does not necessarily represent the decisions or the stated policy of the United Nations Environment Programme, the International Labour Organisation, or the World Health Organization. Published under the joint sponsorship of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization World Health Orgnization Geneva, 1986 The International Programme on Chemical Safety (IPCS) is a joint venture of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization. The main objective of the IPCS is to carry out and disseminate evaluations of the effects of chemicals on human health and the quality of the environment. Supporting activities include the development of epidemiological, experimental laboratory, and risk-assessment methods that could produce internationally comparable results, and the development of manpower in the field of toxicology. Other activities carried out by the IPCS include the development of know-how for coping with chemical accidents, coordination