Pesticide Use and Toxicology in Relation to Wildlife: Organophosphorus and Carbamate , Compounds
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ACEPHATE (Addendum)
3 ACEPHATE (addendum) First draft prepared by Professor P.K. Gupta 1 and Dr Angelo Moretto 2 1 Rajinder Nagar, Bareilly, UP, India; 2 Dipartimento Medicina Ambientale e Sanità Pubblica, Università di Padova, Padova, Italy Explanation..........................................................................................................3 Evaluation for acceptable daily intake.................................................................4 Biochemical aspects ......................................................................................4 Oral absorption, distribution, excretion and metabolism .......................4 Toxicological studies.....................................................................................5 Acute toxicity.........................................................................................5 Short-term studies of toxicity.................................................................6 Special studies........................................................................................7 Studies on inhibition of cholinesterase activity in vitro ..................7 Short-term study of neurotoxicity ...................................................7 Developmental neurotoxicity..........................................................9 Observations in humans ..............................................................................10 Comments..........................................................................................................12 Toxicological evaluation ...................................................................................13 -
12.18 Carbofuran Carbofuran (CAS No
12. CHEMICAL FACT SHEETS WHO (2003) Cadmium in drinking-water. Background document for preparation of WHO Guidelines for drinking-water quality. Geneva, World Health Organization (WHO/SDE/WSH/03.04/80). 12.18 Carbofuran Carbofuran (CAS No. 1563-66-2) is used worldwide as a pesticide for many crops. Residues in treated crops are generally very low or not detectable. The physical and chemical properties of carbofuran and the few data on occurrence indicate that drink- ing-water from both groundwater and surface water sources is potentially the major route of exposure. Guideline value 0.007 mg/litre Occurrence Has been detected in surface water, groundwater and drinking-water, generally at levels of a few micrograms per litre or lower; highest concentration (30 mg/litre) measured in groundwater ADI 0.002 mg/kg of body weight based on a NOAEL of 0.22 mg/kg of body weight per day for acute (reversible) effects in dogs in a short-term (4- week) study conducted as an adjunct to a 13-week study in which inhibition of erythrocyte acetylcholinesterase activity was observed, and using an uncertainty factor of 100 Limit of detection 0.1 mg/litre by GC with a nitrogen–phosphorus detector; 0.9 mg/litre by reverse-phase HPLC with a fluorescence detector Treatment achievability 1 mg/litre should be achievable using GAC Guideline derivation • allocation to water 10% of ADI • weight 60-kg adult • consumption 2 litres/day Additional comments Use of a 4-week study was considered appropriate because the NOAEL is based on a reversible acute effect; the NOAEL will also be protective for chronic effects. -
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) -
488 Subpart A—Organic Pesticide Chemicals Manufacturing
§ 455.11 40 CFR Ch. I (7–1–12 Edition) chemical products and be considered a this subpart are applicable to dis- ‘‘stand-alone’’ PFPR facility. charges resulting from the manufac- ture of the following organic active in- [43 FR 17776, Apr. 25, 1978, as amended at 50 FR 40701, Oct. 4, 1985; 51 FR 44911, Dec. 15, gredients: Aldrin, BHC, Captan, 1986; 58 FR 50689, Sept. 28, 1993; 61 FR 57548, Chlordane, DDD, DDE, DDT, Dichloran, Nov. 6, 1996] Dieldrin, Endosulfan, Endrin, Hepta- chlor, Lindane, Methoxychlor, Mirex, Subpart A—Organic Pesticide PCNB, Toxaphene, Trifluralin, Chemicals Manufacturing Azinphos Methyl, Demeton-O, Demeton-S, Diazinon, Disulfoton, Mal- Subcategory athion, Parathion Methyl, Parathion Ethyl, Aminocarb, Carbaryl, SOURCE: 43 FR 44846, Sept. 29, 1978, unless Methiocarb, Mexacarbate, Propoxur, otherwise noted. Barban, Chlorpropham, Diuron, Fenuron, Fenuron-TCA, Linuron, § 455.11 Compliance date for pretreatment standards for existing Monuron, Monuron-TCA, Neubron, sources (PSES). Propham, Swep, 2,4-D, Dicamba, Silvex, 2,4,5-T, Siduron, Perthane, and All discharges subject to Dicofol. pretreatment standards for existing (c) The intermediates used to manu- sources (PSES) in subparts A and B of facture the active ingredients and ac- this part must comply with the stand- tive ingredients used solely in experi- ards no later than September 28, 1993. mental pesticides are excluded from [61 FR 57549, Nov. 6, 1996] coverage in this subpart. Insecticidal pathogenic organisms such as Bacillus § 455.20 Applicability; description of thuringiensis, insect growth hormones, the organic pesticide chemicals plant extracts such as pyrethrins; sex manufacturing subcategory. attractants and botanicals such as Ro- (a) For the purpose of calculating and tenone are also excluded from BPT applying effluent limitations for COD, coverage in this subpart. -
Comments of Teresa Homan with Attachments
Teresa Homan Watertown, SD 57201 I am a landowner in Deuel County, South Dakota. Our land boarders the Deuel Harvest Wind Project in Deuel county, Docket # EL 18-053. There are 112 towers cited in the project, with 9 towers within a mile of our property. We have spent over three decades developing this property to enhance wildlife and for the enjoyment of our family. Can you imagine how we felt when we found we have a population of eastern bluebirds? We have yellow warblers, which by the way feed on the web worms that form in our trees. We have orioles, cedar waxwings, brown thrashers, rose breasted grosbeaks, gold finches, purple finches, robins, blue jays, nuthatches, eastern kingbirds, bitterns, dark eyed juncos, red winged blackbirds, morning doves, owls, cow birds, northern mocking birds, grey cat birds, wood thrushes, tufted titmouse, king fishers, indigo buntings, scarlet tanagers, bobolinks, meadowlarks, many woodpeckers, turkeys, turkey vultures, even humming birds and bald eagles. There are more, just to numerous to list. Many of these birds we have seen for the first time in our lives on this property in the past 1 O years. Not only are these birds beautiful and fun to watch, they have their purpose in the ecosystem. We also see northern long eared bats, that are on the endangered list in South Dakota. These birds are making a come back after the use of insecticides that nearly wiped out many. In the 1940's the insecticide DDT was introduced for public use, it is now banned from sale. In 1976 the herbicide Roundup was introduced to the public. -
Validation Report 20
EURL for Cereals and Feeding stuff National Food Institute Technical University of Denmark Validation Report 20 Determination of pesticide residues in rice baby food by GC-MS/MS and LC-MS/MS (QuEChERS method) Parvaneh Hajeb Susan Strange Herrmann Mette Erecius Poulsen December 2015 Page 2 of 18 CONTENT: 1. Introduction ...................................................................................................................................... 3 2. Principle of analysis......................................................................................................................... 3 3. Validation design ............................................................................................................................. 4 4. Chromatograms and calibration curves .......................................................................................... 5 5. Validation parameters...................................................................................................................... 9 6. Criteria for the acceptance of validation results ........................................................................... 10 7. Results and discussion ................................................................................................................... 10 8. Conclusions .................................................................................................................................... 12 9. References ..................................................................................................................................... -
Oxydemeton-Methyl (166) Demeton-S-Methyl (073
oxydemeton-methyl 993 OXYDEMETON-METHYL (166) DEMETON-S-METHYL (073) EXPLANATION Oxydemeton-methyl (ODM) was evaluated for residues by the JMPR in 1968, 1973, 1979, 1984, 1989, and 1992. The 1992 review was a complete re-evaluation. It reviewed extensive residue data from supervised trials on all major crops and associated data on use patterns, storage stability, processing, and methods of residue analysis were reviewed and numerous MRLs were recommended. The MRLs are expressed as the sum oxydemeton-methyl, demeton-S-methyl, and demeton-S- methylsulphon, expressed as oxydemeton-methyl. The ADI was established in 1989 at 0.0003 mg/kg body weight and is for the sum of the three compounds. Demeton-S-methyl is an insecticide. The sulfoxide of demeton-S-methyl is ODM. It currently has no MRLs. The 1995 CCPR scheduled ODM and demeton-S-methyl for periodic review of residue aspects by the 1997 JMPR (ALINORM 95/24A). This was changed by the 1997 CCPR, which scheduled ODM and demeton-S-methyl for periodic review by the 1998 JMPR. Bayer AG has submitted data in support of the Periodic Review which included information on crops and regions of interest to that company. The governments of Germany and The Netherlands have also submitted information. IDENTITY Common name (ISO): Oxydemeton-methyl Chemical name: IUPAC: S-2-ethylsulfinylethyl O,O-dimethyl phosphothioate CA: S-[2-ethylsulfinyl)ethyl] O,O-dimethyl phosphothioate CAS number: 301-12-2 EU-index number: 015-046-00-7 EINECS number: 206-110-7 CIPAC number: 171 Molecular formula: C6 H15 O4 P S2 Synonyms: Metasystox R Structural formula: . -
Florida State Emergency Response Commission
Florida State Emergency Response Commission Sub-Committee on Training (SOT) HAZARDOUS MATERIALS MEDICAL TREATMENT PROTOCOLS Version 3.3 TOXIDROMES Toxidromes are clinical syndromes that the patient presents with. These patterns of signs and symptoms are essential for the successful recognition of chemical exposure. The toxidromes identified in this protocol are chemical exposure based while others such as the opioids are found within general medical protocol. These chemical toxidromes are identified clinically into five syndromes: Irritant Gas Toxidrome Asphyxiant Toxidrome Corrosive Toxidrome Hydrocarbon and Halogenated Hydrocarbons Toxidrome Cholinergic Toxidrome Each can present as a clinical manifestation of the chemical/poisoning involved with some cross-over between toxidromes. This list combines the toxic syndromes found within NFPA 473 (A.5.4.1(2) and traditional syndromes. Toxidrome Correlation to NFPA Standard 473 and Traditional Syndromes Toxidrome NFPA 473 A.5.4.1(2) Hazardous Materials Protocol Correlation Irritant Gas (j) Irritants Bronchospasm OC Pepper spray & lacrimants Asphyxiant (c) Chemical asphyxiants Carbon Monoxide (d) Simple asphyxiants Aniline dyes, Nitriles, Nitrares (h) Blood Agents Cyanide & Hydrogen Sulfide (n) Nitrogen Compounds Closed Space Fires Simple Asphyxants Corrosive (a) Corrosives Hydrofluroic Acid (g) Vesicants Chemical burns to the eye Choramine and Chlorine Hydrocarbon (e) Organic solvents Phenol and (q) Phenolic Compounds Halogenated Hydrocarbons Halogenated Hydrocarbons Cholinergic (b) Pesticides -
Comparison of Acute Noaels and Benchmark Doses for Female Brain Cholinesterase Inhibition
Supplemental Material for: February 5-8, 2002 SAP 25 January 2002 Comparison of Acute NOAELs and Benchmark Doses for Female Brain Cholinesterase Inhibition In cumulative risk assessment, it is important to characterize both the time frame for exposure (e.g., What is the exposure duration?) and for the toxic effect (e.g., What are the time to peak effects and the time to recovery?). In the Preliminary Cumulative Risk Assessment of the Organophoshate Pesticides (OPs) relative potency factors (RPFs) for 29 chemicals and points of departure (PODs) and the index chemical were determined based on whole brain cholinesterase (ChE) data from toxicity studies of 21 days and longer. The Office of Pesticide Programs has argued that the use of steady state data for relative potency determination generates relative potency factors (RPFs) that are reproducible and reflect less variability than RPFs derived from single-dose or short-term studies where the extent of inhibition changes rapidly immediately following dosing. OPP has posed a question to the FIFRA SAP for the February 5-8, 2002 review concerning how best to evaluate risk, taking into account the temporal characteristics of the hazard endpoint (i.e., cholinesterase inhibition) and the temporal characteristics of the exposure patterns for the food, drinking water, and residential/nonoccupational pathways. In order to facilitate the panel discussion, a table listing the available single dose toxicity studies performed with OPs has been made. Most of the studies are acute neurotoxicity (ACN) studies (OPPT Guideline 870.6200, OPP Guideline 81-8) administered by gavage. Acute lethality studies were not included. Dose levels, no- observed-adverse-effect levels (NOAELs), and no-observed-adverse-effect levels (LOAELs) for female brain ChE are also listed in the table. -
The Spruce Budworm, Choristoneura Fumiferana
02-01370 Spruce Budworm Bro 10/10/02 11:09 AM Page 1 MORE INFORMATION The he spruce budworm, Choristoneura fumiferana For more information on Spruce Budworms call: The Tree Line Spruce (Clemens), is the most destructive and widely (204) 945-7866. Or write: Budworm distributed forest defoliator in North America. Manitoba Conservation Forestry Branch In Manitoba T Forest Health and Ecology The destructive phase of this pest is the larval or caterpillar 200 Saulteaux Crescent Winnipeg, Manitoba R3J 3W3 stage. Massive budworm outbreaks occur periodically, Web site: www.gov.mb.ca/natres/forestry/ destroying hundreds of thousands of hectares of valuable fir and spruce. Aerial view of budworm damage In eastern Canada the budworm’s preferred food is balsam fir, Photos courtesy of Canadian Forest Service, Great Lakes Forest Research Centre, white spruce and red spruce. In Manitoba, the budworm Sault Ste. Marie, Ontario and Northern Forest Research Centre, Edmonton, Alberta. feeds primarily on white spruce and balsam fir, and, less frequently, on black spruce. 02-01370 Spruce Budworm Bro 10/10/02 11:09 AM Page 2 DESCRIPTION OF LIFE STAGES LIFE CYCLE DAMAGE CONTROL The adult moth has a wingspread of The female moth lays In light and moderate infestations Various insecticides are used 21 to 30 mm. It is grey-brown in its eggs in July on the damage is restricted to a partial against the spruce budworm to colour with silvery white patches on underside of needles. loss of new foliage, particularly in protect valuable spruce and fir the forewings. Normally, the eggs the upper crown trees. -
Organophosphate Poisoning : a Review
120 Sinha and Sharma Med J Indones Organophosphate poisoning : A review Parmod K. Sinha, Ashok Sharma Abstrak Pestisida organofosfat digunakan secara luas di seluruh dunia. Keracunan oleh bahan ini merupakan masalah kesehatan masyarakat, terutama di negara berkembang. Zat neurotoksik organofosfat merupakan bahan yang dianggap mengancam dalam bidang militer dan terorisme. Mekanisme toksisitas bahan ini adalah dengan cara menghambat asetilkolinesterase yang mengakibatkan menumpuknya neurotransmitor asetilkolin dan terjadi rangsangan terus-menerus pada reseptor asetilkolin pada sistem saraf sentral maupun perifer. Selain krisis kolinergik, organofosfat dapat menimbulkan berbagai sindrom neurologis, baik akut maupun kronik. Sedangkan gejala peralihan ( intermediate) terjadi 1-4 hari setelah krisis kolinergik teratasi. Pengobatan standar terdiri dari reaktivasi asetilkolinesterase dengan antidot golongan oksim (prolidoksim, oksidoksime, HI-6 dan HLo7), dan pengendalian efek biokimia asetilkolin dengan menggunakan atropin. Golongan oksim yang baru HI-6 dan Hlo7 merupakan reaktivator asetilkolinesterase yang lebih cocok dan efektif untuk keracunan akut dan berat dibandingkan dengan prolidoksim dan obidoksim. Penderita yang mendapat pengobatan segera, biasanya dapat sembuh dari toksisitas akut, namun gejala neurologis ikutan dapat saja terjadi. (Med J Indones 2003; 12: 120-6) Abstract Organophosphate pesticides are used extensively worldwide, and poisoning by these agents, particularly in developing nations is a public health problem. Organophosphorous -
Chlorpyrifos (Dursban) Ddvp (Dichlorvos) Diazinon Malathion Parathion
CHLORPYRIFOS (DURSBAN) DDVP (DICHLORVOS) DIAZINON MALATHION PARATHION Method no.: 62 Matrix: Air Procedure: Samples are collected by drawing known volumes of air through specially constructed glass sampling tubes, each containing a glass fiber filter and two sections of XAD-2 adsorbent. Samples are desorbed with toluene and analyzed by GC using a flame photometric detector (FPD). Recommended air volume and sampling rate: 480 L at 1.0 L/min except for Malathion 60 L at 1.0 L/min for Malathion Target concentrations: 1.0 mg/m3 (0.111 ppm) for Dichlorvos (PEL) 0.1 mg/m3 (0.008 ppm) for Diazinon (TLV) 0.2 mg/m3 (0.014 ppm) for Chlorpyrifos (TLV) 15.0 mg/m3 (1.11 ppm) for Malathion (PEL) 0.1 mg/m3 (0.008 ppm) for Parathion (PEL) Reliable quantitation limits: 0.0019 mg/m3 (0.21 ppb) for Dichlorvos (based on the RAV) 0.0030 mg/m3 (0.24 ppb) for Diazinon 0.0033 mg/m3 (0.23 ppb) for Chlorpyrifos 0.0303 mg/m3 (2.2 ppb) for Malathion 0.0031 mg/m3 (0.26 ppb) for Parathion Standard errors of estimate at the target concentration: 5.3% for Dichlorvos (Section 4.6.) 5.3% for Diazinon 5.3% for Chlorpyrifos 5.6% for Malathion 5.3% for Parathion Status of method: Evaluated method. This method has been subjected to the established evaluation procedures of the Organic Methods Evaluation Branch. Date: October 1986 Chemist: Donald Burright Organic Methods Evaluation Branch OSHA Analytical Laboratory Salt Lake City, Utah 1 of 27 T-62-FV-01-8610-M 1.