Pesticide Leachability Chart
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MN2000 FSAC 006 Revised1978.Pdf
-i .., ,,, (I-,~-- -' d ~-- C:::- ,, AG RIC UL TURAL EXTENSION SERVICE Afr{ ,<"·<,'>· , -> ',' "\, '. '' ~'¥) AGRICULTURAL CHEMICALS FACT SHEET No. 6-1978 Chemicals for'Weed Cop: GERALD R. MILLER . \~:::sr" This fact sheet is intended only as a summary of suggested Herbicide names and formulations alternative chemicals for weed control in corn. Label informa Common Trade Concentration and tion should be read and followed exactly. For further informa name name commercial formulation 1 tion, see Extension Bulletin 400, Cultural and Chemical Weed Control in Field Crops. Alachlor Lasso 4 lb/gal L Lasso 11 15% G Selection of an effective chemical or combination of chemicals Atrazine AAtrex, 80% WP, 4 lb/gal L should be based on consideration of the following factors: others 80%WP -Clearance status of the chemical Atrazine and propachlor AAtram 20% G -Use of the crop Bentazon Basagran 4 lb/gal L -Potential for soil residues that may affect following crops Butylate and protectant Sutan+ 6.7 lb/gal L -Kinds of weeds Cyanazine Bladex 80% WP, 15% G, 4 lb/gal L -Soil texture Dicamba Banvel 4 lb/gal L -pH of soil Dicamba and 2,4-D Banvel-K 1.25 lb/gal dicamba -Amount of organic matter in the soil 2.50 lb/gal 2,4-D -Formulation of the chemical EPTC and protectant Eradicane 6.7 lb/gal L -Application equipment available Linuron Lorox 50%WP -Potential for drift problems Metolachlor Dual 6 lb/gal L Propachlor Bexton, 65% WP, 20% G, 4 lb/gal L Ramrod 2,4-D Several Various 1 G = granular, L = liquid, WP= wettable powder Effectiveness of herbicides on -
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. -
USDA, Forest Service Forest Health Protection GSA Contract No
SERA TR 02-43-13-03b Triclopyr - Revised Human Health and Ecological Risk Assessments Final Report Prepared for: USDA, Forest Service Forest Health Protection GSA Contract No. GS-10F-0082F USDA Forest Service BPA: WO-01-3187-0150 USDA Purchase Order No.: 43-1387-2-0245 Task No. 13 Submitted to: Dave Thomas, COTR Forest Health Protection Staff USDA Forest Service Rosslyn Plaza Building C, Room 7129C 1601 North Kent Street Arlington, VA 22209 Submitted by: Patrick R. Durkin Syracuse Environmental Research Associates, Inc. 5100 Highbridge St., 42C Fayetteville, New York 13066-0950 Telephone: (315) 637-9560 Fax: (315) 637-0445 E-Mail: [email protected] Home Page: www.sera-inc.com March 15, 2003 TABLE OF CONTENTS LIST OF APPENDICES ...................................................... iv LIST OF WORKSHEETS ...................................................... v LIST OF ATTACHMENTS .................................................... v LIST OF TABLES ............................................................ v LIST OF FIGURES ......................................................... viii ACRONYMS, ABBREVIATIONS, AND SYMBOLS .............................. ix COMMON UNIT CONVERSIONS AND ABBREVIATIONS ......................... xi CONVERSION OF SCIENTIFIC NOTATION .................................... xii EXECUTIVE SUMMARY ................................................... xiii 1. INTRODUCTION ........................................................ 1-1 2. PROGRAM DESCRIPTION ................................................ 2-1 2.1. OVERVIEW -
Atrazine Active Ingredient Data Package April 1, 2015
Active Ingredient Data Package ATRAZINE Version #5 (May 14, 2015) Long Island Pesticide Pollution Prevention Strategy Active Ingredient Assessment Bureau of Pest Management Pesticide Product Registration Section Contents 1.0 Active Ingredient General Information – Atrazine .................................................................... 3 1.1 Pesticide Type ........................................................................................................................... 3 1.2 Primary Pesticide Uses .............................................................................................................. 3 1.3 Registration History .................................................................................................................. 3 1.4 Environmental Fate Properties ................................................................................................. 3 1.5 Standards, Criteria, and Guidance ............................................................................................ 4 2.0 Active Ingredient Usage Information ........................................................................................ 5 2.1 Reported Use of Atrazine in New York State ............................................................................ 5 2.2 Overall Number and Type of Products Containing the Active Ingredient ................................ 7 2.3 Critical Need of Active Ingredient to Meet the Pest Management Need of Agriculture, Industry, Residents, Agencies, and Institutions ...................................................................... -
Herbicide Mode of Action Table High Resistance Risk
Herbicide Mode of Action Table High resistance risk Chemical family Active constituent (first registered trade name) GROUP 1 Inhibition of acetyl co-enzyme A carboxylase (ACC’ase inhibitors) clodinafop (Topik®), cyhalofop (Agixa®*, Barnstorm®), diclofop (Cheetah® Gold* Decision®*, Hoegrass®), Aryloxyphenoxy- fenoxaprop (Cheetah®, Gold*, Wildcat®), fluazifop propionates (FOPs) (Fusilade®), haloxyfop (Verdict®), propaquizafop (Shogun®), quizalofop (Targa®) Cyclohexanediones (DIMs) butroxydim (Factor®*), clethodim (Select®), profoxydim (Aura®), sethoxydim (Cheetah® Gold*, Decision®*), tralkoxydim (Achieve®) Phenylpyrazoles (DENs) pinoxaden (Axial®) GROUP 2 Inhibition of acetolactate synthase (ALS inhibitors), acetohydroxyacid synthase (AHAS) Imidazolinones (IMIs) imazamox (Intervix®*, Raptor®), imazapic (Bobcat I-Maxx®*, Flame®, Midas®*, OnDuty®*), imazapyr (Arsenal Xpress®*, Intervix®*, Lightning®*, Midas®* OnDuty®*), imazethapyr (Lightning®*, Spinnaker®) Pyrimidinyl–thio- bispyribac (Nominee®), pyrithiobac (Staple®) benzoates Sulfonylureas (SUs) azimsulfuron (Gulliver®), bensulfuron (Londax®), chlorsulfuron (Glean®), ethoxysulfuron (Hero®), foramsulfuron (Tribute®), halosulfuron (Sempra®), iodosulfuron (Hussar®), mesosulfuron (Atlantis®), metsulfuron (Ally®, Harmony®* M, Stinger®*, Trounce®*, Ultimate Brushweed®* Herbicide), prosulfuron (Casper®*), rimsulfuron (Titus®), sulfometuron (Oust®, Eucmix Pre Plant®*, Trimac Plus®*), sulfosulfuron (Monza®), thifensulfuron (Harmony®* M), triasulfuron (Logran®, Logran® B-Power®*), tribenuron (Express®), -
Exposure to Herbicides in House Dust and Risk of Childhood Acute Lymphoblastic Leukemia
Journal of Exposure Science and Environmental Epidemiology (2013) 23, 363–370 & 2013 Nature America, Inc. All rights reserved 1559-0631/13 www.nature.com/jes ORIGINAL ARTICLE Exposure to herbicides in house dust and risk of childhood acute lymphoblastic leukemia Catherine Metayer1, Joanne S. Colt2, Patricia A. Buffler1, Helen D. Reed3, Steve Selvin1, Vonda Crouse4 and Mary H. Ward2 We examine the association between exposure to herbicides and childhood acute lymphoblastic leukemia (ALL). Dust samples were collected from homes of 269 ALL cases and 333 healthy controls (o8 years of age at diagnosis/reference date and residing in same home since diagnosis/reference date) in California, using a high-volume surface sampler or household vacuum bags. Amounts of agricultural or professional herbicides (alachlor, metolachlor, bromoxynil, bromoxynil octanoate, pebulate, butylate, prometryn, simazine, ethalfluralin, and pendimethalin) and residential herbicides (cyanazine, trifluralin, 2-methyl-4- chlorophenoxyacetic acid (MCPA), mecoprop, 2,4-dichlorophenoxyacetic acid (2,4-D), chlorthal, and dicamba) were measured. Odds ratios (OR) and 95% confidence intervals (CI) were estimated by logistic regression. Models included the herbicide of interest, age, sex, race/ethnicity, household income, year and season of dust sampling, neighborhood type, and residence type. The risk of childhood ALL was associated with dust levels of chlorthal; compared to homes with no detections, ORs for the first, second, and third tertiles were 1.49 (95% CI: 0.82–2.72), 1.49 (95% CI: 0.83–2.67), and 1.57 (95% CI: 0.90–2.73), respectively (P-value for linear trend ¼ 0.05). The magnitude of this association appeared to be higher in the presence of alachlor. -
FSC-TPL-01-002 Application for a Derogation to Use a Highly Hazardous Pesticide
FSC-TPL-01-002 Application for a derogation to use a highly hazardous pesticide. 2,4-D, 2-ethylhexyl ester Name and contact details of SCS certification body requesting Dave Wager derogation: [email protected] 510 251-7049 To be completed at the national level Active ingredient for which derogation requested: Geographical scope of All states of USA requested derogation: Is there an accredited or preliminarily accredited FSC FSC US standard Forest Stewardship Standard applicable to the territory concerned? Requested time period for derogation: 5 years (nb Derogations shall normally be issued for a five-year period. There will be a presumption against renewal of a derogation after the expiry of the five-year period). 1. Demonstrated need Need may be demonstrated where: - The pesticide is used for protecting native species and forests against damage caused by introduced species or for protecting human health against dangerous diseases, OR - Use of the pesticide is obligatory under national laws or regulations, OR - Use of the pesticide is the only economically, environmentally, socially and technically feasible way of controlling specific organisms which are causing severe damage in natural forests or plantations in the specified country (as indicated by consideration, assessments and preferably field-trials of alternative non- chemical or less toxic pest-management methods) Explain how the proposed use complies with the specified criteria for need, including the consideration of alternatives which do not require the use of pesticides on the FSC list of ‘highly hazardous pesticides’: Overview 2,4-D ester is a selective herbicide used to control broad leaved plants such as woody species and forbs. -
Triclopyr Human Health and Ecological Risk Assessment Corrected Final Report
SERA TR-052-25-03c Triclopyr Human Health and Ecological Risk Assessment Corrected Final Report Submitted to: Paul Mistretta, COR USDA/Forest Service, Southern Region 1720 Peachtree RD, NW Atlanta, Georgia 30309 USDA Forest Service Contract: AG-3187-C-06-0010 USDA Forest Order Number: AG-43ZP-D-09-0034 SERA Internal Task No. 52-25 Submitted by: Patrick R. Durkin Syracuse Environmental Research Associates, Inc. 8125 Solomon Seal Manlius, New York 13104 Fax: (315) 637-0445 E-Mail: [email protected] Home Page: www.sera-inc.com May 24, 2011 October 20, 2011 (Minor Correction) July 9, 2016 (Corrections) Error Notes October 20, 2011 In the original release of the final report (SERA TR-052-25-03a dated May 24, 2011), Tables 2 and 22 incorrectly listed the water solubility of TCP as 100 mg/L. As indicated in Table 1, the correct value, from Knuteson (1999), is 49,000 mg/L. This error was noted by Dr. K. King (U.S. Fish and Wildlife Service). The error has been corrected. While the Gleams-Driver runs were made using the 100 mg/L water solubility, re-runs using the water solubility of 49,000 mg/L yielded results that are indistinguishable from the original runs. Thus, the appendices have not been change. Water solubility is not a sensitive parameter in GLEAMS unless the soil water is saturated. This did not occur in the Gleams-Driver modeling. July 9, 2016 During an audit of WorksheetMaker (Version 6.00.15), it was noted that the chronic toxicity values of TCP to aquatic invertebrates had been entered incorrectly into the WorksheetMaker database and the aquatic toxicity values of TCP for algae had been omitted. -
Special Report 354 April 1972 Agricultural Experiment Station
ORTMAL DO ;10T REMOVE 7.9 m FILE Special Report 354 April 1972 Agricultural Experiment Station Oregon State University, Corvallis I FIELD APPLICATION OF HERBICIDES--AVOIDING DANGER TO FISH Erland T. Juntunen Department of Fisheries and Wildlife Oregon State University Corvallis, Oregon and Logan A. Norris Pacific Northwest Forestry Sciences Laboratory and Range Experiment Station Forest Service, U. S. Department of Agriculture Corvallis, Oregon April, 1972 Trade names are used in this publication solely to provide specific information. No endorsement of products is intended nor is criticism implieLl to products mentioned or omitted. Recommendations are not made concerning safe use of products nor is any guarantee or warranty of results or effects of the products intended or implied. ii Chemical weed and brush control with herbicides is an important land management practice in modern agriculture and forestry. In some cases, herbicides are applied directly to bodies of water for aquatic weed control. More commonly, herbicides are applied to lands adjacent to waterways for general weed and brush control. The responsible applicator will avoid damage to fishery resources by being fully aware of a particular herbicides potential hazard to fish. Herbicide applications should be considered hazardous to fish when there is the probability fish will be exposed to herbicide concen- trations which are harmful. This bulletin offers information that will aid in selecting the particular herbicides and formulations of least hazard to fish considering the toxicity of the herbicide and the poten- tial for its entry into streams, lakes, or ponds. Entry of Herbicides into the Aquatic Environment In aquatic weed control, the effective concentration of herbicide in the water depends on the rate of application, the rate of the spread of the chemical, the size and chemical composition of the body of water, the rate of degradation or adsorption of the chemical on sediments, and the rate of mixing of treated water with untreated water. -
MC(' Potential Exposure of Humans to 2
(MC( FUNDAMENTAL AND APPLIED TOXICOLOGY 1:3 3 9-3 4 6 (1981) Potential Exposure of Humans to 2,4,5-T and TCDD in the Oregon Coast Ranges MICHAEL NEWTON" and LOGAN A. NORRISB "Professor of Forest Ecology, Oregon State University, Corvallis; BChief Research Chemist, USDA Forest Service, Corvallis, Oregon ABSTRACT Potential Exposure of Humans to 2,4,5-T and TCDD in Humans may be exposed to herbicides through drift; inges- the Oregon Coast Ranges. Newton, M. and Norris, L.A. tion of wild and domestic meat, vegetables, and fruit; con- (1981). F.undam. AppL Toxicol. 1:339-346. Research on the sumption of water; and dermal contact while handling the use of 2,4,5-trichlorophenoxyacetic acid (2,4,5-T) contami- chemicals, equipment, and treated vegetation. The range of -8 nated with 2.5 X 10 parts 2,3,7,8-tetrachlorodibenzo-p- potential exposure extends from zero, if there is no encounter dioxin (TCDD) in forests of the Oregon Coast Ranges per- with the herbicide, to the worst situation where the person has mits estimates of human exposures for both compounds. encountered the highest levels of water contamination, drift Estimated total exposure of nearby ( ^ 1/8 mile distant) resi- exposure, meat contamination, and dermal exposure simul- dents during the first week after application is 0.0039 mg/kg taneously. We have brought estimates of all sources together of 2,4,5-T for a 70-kg adult. Exposure to TCDD in the same to determine the possible range of total exposure from episode would be 1.9 X 10 b ° mg/kg. -
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 -
CAS No.) Screening Justification Is Public Comment Now Open? CAS No
EGLE Air Quality Division (AQD) Air Toxics Screening Level Justifications (Numerically by CAS No.) Screening Justification Is Public Comment Now Open? CAS No. Chemical Name Level & Responses Info E-Mail AQD Deadline None ad acid View View Not Open for Public Comment None amyl acetate (mixture) View View Not Open for Public Comment None atlox 848 View View Not Open for Public Comment None biosam tp-1.5 View View Not Open for Public Comment None calcium chloride View View Not Open for Public Comment None epoxy resin solution View View Not Open for Public Comment None heptamethyl-1-vinyl-1,7-dichlorotetrasilazane View View Not Open for Public Comment None n-butylglucamine View View Not Open for Public Comment None n-chloro-2,6-difluorobenzamide View View Not Open for Public Comment None trichloroethylene View View Not Open for Public Comment None triethylammonium suleptanate View View Not Open for Public Comment 50-00-0 formaldehyde View View Not Open for Public Comment 50-03-3 hydrocortisone acetate View View Not Open for Public Comment 50-21-5 lactic acid View View Not Open for Public Comment 50-28-2 estradiol View View Not Open for Public Comment 50-29-3 ddt View View Not Open for Public Comment 50-32-8 benzo(a)pyrene View View Not Open for Public Comment 51-28-5 2,4-dinitrophenol View View Not Open for Public Comment 53-36-1 methyl predisolone acetate View View Not Open for Public Comment 53-70-3 dibenz(a,h)anthracene View View Not Open for Public Comment 56-23-5 carbon tetrachloride View View Not Open for Public Comment 56-49-5 3-methylcholanthrene View View Not Open for Public Comment 56-55-3 benz(a)anthracene View View Not Open for Public Comment 56-81-5 glycerol View View Not Open for Public Comment 57-11-4 stearic acid View View Not Open for Public Comment Revised Monday, September 27, 2021 Page 1 of 51 EGLE Air Quality Division (AQD) Air Toxics Screening Level Justifications (Numerically by CAS No.) Screening Justification Is Public Comment Now Open? CAS No.