Evaluation of P-Hydroxyphenylpyruvate Dioxygenase-Inhibiting Herbicides for Controlling Mugwort
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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. -
July 6, 2020 OPP Docket Environmental Protection Agency Docket Center (EPA/DC), (28221T) 1200 Pennsylvania Ave. NW Washington
July 6, 2020 OPP Docket Environmental Protection Agency Docket Center (EPA/DC), (28221T) 1200 Pennsylvania Ave. NW Washington, DC 20460-000 Docket ID # EPA-HQ-OPP-2014-0167 Re. Clopyralid, Case Number 7212 Dear Madam/Sir: These comments are submitted on behalf of Beyond Pesticides, Beyond Toxics, Center for Food Safety, Hawai’i Alliance for Progressive Action, Hawai'i SEED, LEAD for Pollinators, Maine Organic Farmers and Gardeners Association, Maryland Pesticide Education Network, Northeast Organic Farming Association—Massachusetts Chapter, Northwest Center for Alternatives to Pesticides, People and Pollinators Action Network, Real Organic Project, Sierra Club, Toxic Free NC, Women’s Voices for the Earth. Founded in 1981 as a national, grassroots, membership organization that represents community-based organizations and a range of people seeking to bridge the interests of consumers, farmers and farmworkers, Beyond Pesticides advances improved protections from pesticides and alternative pest management strategies that reduce or eliminate a reliance on pesticides. Our membership and network span the 50 states and the world. EPA’s proposed interim decision (PID) on the weed killer clopyralid is inadequate to protect property, nontarget plants, and pollinators from exposure to the chemical. Clopyralid poses unreasonable adverse effects that cannot be remedied by EPA’s proposed fixes. It should not be reregistered. Clopyralid has a long history of causing environmental and property damage through drift, runoff, use of treated plant material (such as straw or grass clippings) for mulch or compost, contaminated irrigation water, and urine or manure from animals consuming treated vegetation. Clopyralid (3,6-dichloro-2-pyridinecarboxylic acid) is an herbicide used to control broadleaf weeds on nonresidential lawns and turf, range, pastures, right-of ways and on several crops. -
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 -
U.S. EPA, Pesticide Product Label, CLOPYRALID MEA+2,4-D, 07/07/2008
'f-;) 7 S-O - 'ta- \ ENVIRONMENTAL PROTECTION u.s. EPA Reg, Nwnber: Date of Issuance: AGENCY Office of Pesticide Programs 42750-92 Registration Division (7505P) -- 7 JtJL 2DOB Ariel Rios, Building 1200 Pennsylvania Ave., NW Washington, D.C, 20460 NOTICE OF PESTICIDE: Term of Issuance: _ Registration -X Reregistration Name of Pesticide Product: (under FIFRA, as amended) Clopyralid MEA+ 2,4- D Name and Address of Registrant (include ZIP Code): Albaugh, Inc. 121 NE 18th Street Ankeny, IA 50021 N o~e: C.h~nge,~itiIflb~ljllgl,~i:t1~1i~~J9~~~1?~!iUiC~,fJqnf.th~i.:~G~~t~4j#'qqHriet£i~riw,ii4;tl}is, :' ',' ,,',: " registratio"n ~4stl>e ,s~Drriittedto,aPQjl,~9:~pt~qby 'theRe,gi~ttatipn pivisi()i1 prior t9 ':tI~.~"Qn~~)*~eI , ,~:~~~~r:::~.~:;~~:1~~jJ:r~,2t.edf.~,~.&.~~lt;'~I~\~i,~tfl%~~~i;m)~t~~:;'~~/~~·?~~:,)~·¥'t·.'~~~i,~j~:~:i)~.:,;" ,.".;,' "' On the basis of information furnished by the registrant, the above named pesticide is hereby registered/reregistered under the Federal Insecticide, Fungicide and Rodenticide Act. Registration is in no way to be construed as an endorsement or recommendation of this product by the Agency. In order to protect health and the environment, the Administrator, on his motion, may at any time suspend or cancel the registration of a pesticide in accordance with the Act. The acceptance of any name in connection with the registration of a product under this Act is not to be construed as giving the registrant a right to exclusive use of the name or to its use ifit has been covered by others. This product is reregistered in accordance with FIFRA sec. -
Corn and Soybean Mode of Action Herbicide Chart
By Premix Corn and Soybean This chart lists premix herbicides alphabetically by their trade names so you can identify the premix’s component herbicides and their respective site of action groups. Refer Herbicide Chart to the Mode of Action chart for more information. Component Repeated use of herbicides with the same Site of Premix Trade Active Action site of action can result in the development of Trade Name ® Name ® Ingredient Group* herbicide-resistant weed populations. Authority First ............... Spartan sulfentrazone 14 FirstRate cloransulam 2 Axiom ........................... Define flufenacet 15 This publication was designed for commercial printing, color shifts may occur on other printers and on-screeen. Sencor metribuzin 5 Basis . ........................... Resolve rimsulfuron 2 Harmony GT thifensulfuron 2 By Mode of Action (effect on plant growth) Bicep II Magnum .......... Dual II Magnum s-metolachlor 15 AAtrex atrazine 5 This chart groups herbicides by their modes of action to assist Bicep Lite II Magnum .... Dual II Magnum s-metolachlor 15 AAtrex atrazine 5 you in selecting herbicides 1) to maintain greater diversity in Boundary ...................... Dual Magnum s-metolachlor 15 herbicide use and 2) to rotate among herbicides with different Sencor metribuzin 5 Breakfree ATZ ............... Breakfree acetochlor 15 sites of action to delay the development of herbicide resistance. atrazine atrazine 5 Breakfree ATZ Lite ........ Breakfree acetochlor 15 Number of atrazine atrazine 5 resistant weed Buctril + Atrazine ......... Buctril bromoxynil 6 atrazine atrazine 5 species in U.S. Bullet ............................ Micro-Tech alachlor 15 Site of Chemical Active atrazine atrazine 5 Action Product Examples Camix ........................... Callisto mesotrione 28 Group* Site of Action Family Ingredient (Trade Name ®) Dual II Magnum s-metolachlor 15 Lipid Canopy DF .................. -
Clopyralid 7B.1
Clopyralid 7b.1 CLOPYRALID M. Tu, C. Hurd, R. Robison & J.M. Randall Herbicide Basics Synopsis Clopyralid is an auxin-mimic type herbicide. It is more Chemical formula: 3,6- selective (kills a more limited range of plants) than some dichloro-pyridinecarboxylic other auxin-mimic herbicides like picloram, triclopyr, or acid 2,4-D. Like other auxin-mimics, it has little effect on grasses and other monocots, but also does little harm to Herbicide Family: members of the mustard family (Brassicaceae) and several Pyridine (Picolinic Acid) other groups of broad-leaved plants. Clopyralid controls Target weeds: annual and many annual and perennial broadleaf weeds, particularly of perennial broadleaf weeds, esp. the Asteraceae (sunflower family), Fabaceae (legume knapweeds, thistles, and other family), Solanaceae (nightshade family), Polygonaceae members of the sunflower, (knotweed family), and Violaceae (violet family). It is legume, and knotweed families chemically similar to picloram, but clopyralid has a shorter half-life, is more water-soluble, and has a lower adsorption Forms: salt & ester capacity than picloram. Clopyralid’s half-life in the Formulations: SL, WG environment averages one to two months and ranges up to one year. It is degraded almost entirely by microbial Mode of Action: Auxin mimic metabolism in soils and aquatic sediments. Clopyralid is not Water Solubility: 1,000 ppm degraded by sunlight or hydrolysis. The inability of clopyralid to bind with soils and its persistence implies that Adsorption potential: low clopyralid has the potential to be highly mobile and a Primary degradation mech: contamination threat to water resources and non-target plant Slow microbial metabolism species, although no extensive offsite movement has been documented. -
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. -
U.S. Geological Survey National Water-Quality Assessment Program
U.S. Geological Survey National Water-Quality Assessment Program Stream water-quality analytes Major ions and trace elementsschedule 998 (20 constituents) Pesticides schedule 2437 (229 compounds) Alkalinity 1H1,2,4Triazole Arsenic 2,3,3Trichloro2propene1sulfonic acid (TCPSA) Boron 2,4D Calcium 2(1Hydroxyethyl)6methylaniline Chloride 2[(2Ethyl6methylphenyl)amino]1propanol Fluoride 2AminoNisopropylbenzamide Iron 2Aminobenzimidazole Lithium 2Chloro2',6'diethylacetanilide 2Chloro4,6diaminostriazine {CAAT} Magnesium (Didealkylatrazine) pH 2Chloro4isopropylamino6aminostriazine Potassium 2Chloro6ethylamino4aminostriazine {CEAT} Total dissolved solids 2ChloroN(2ethyl6methylphenyl)acetamide Selenium 2Hydroxy4isopropylamino6aminostriazine 2Hydroxy4isopropylamino6ethylaminostriazin Silica e {OIET} Sodium 2Hydroxy6ethylamino4aminostriazine Specific conductance 2Isopropyl6methyl4pyrimidinol Strontium 3,4Dichlorophenylurea Sulfate 3Hydroxycarbofuran Turbidity 3Phenoxybenzoic acid Vanadium 4(Hydroxymethyl)pendimethalin 4Chlorobenzylmethyl sulfoxide Suspended sediment 4Hydroxy molinate 4Hydroxychlorothalonil Nutrientsschedule 2430 (18 constituents) 4Hydroxyhexazinone A Inorganic carbon, suspended Acephate Dissolved inorganic carbon Acetochlor ammonia + organic nitrogen (unfilteredKjeldahl) Acetochlor oxanilic acid ammonia + organic nitrogen (filteredKjeldahl) Acetochlor sulfonic acid Ammonia as N, filtered Acetochlor sulfynilacetic acid nitrite, filtered Alachlor -
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. -
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