Suggested Herbicide Mixtures for Roadside Vegetation Management
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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, -
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. -
Environmental Fate of Imidazolinone Herbicides and Their Enantiomers
Title Environmental Fate of Imidazolinone Herbicides and Their Enantiomers in Soil and Water Mohammadkazem Ramezani B.Sc. Agronomy, M.Sc. Weed Science This thesis is presented for the degree of Doctorate of Philosophy of the University of Adelaide School of Agriculture, Food & Wine The University of Adelaide Waite Campus, South Australia 2007 Declaration This work contains no material which has been accepted for the award of any other degree or diploma in any university or other tertiary institution and, to the best of my knowledge and belief, contains no material previously published or written by another person, except where due reference has been made in the text. I give consent to this copy of my thesis, when deposited in the University Library, being made available for loan and photocopying. Mohammadkazem Ramezani ii Abstract Imidazolinones represent a new class of herbicides with low mammalian toxicity that can be used at low application rates, either pre- or post-emergence for the control of a wide range of weeds in broadleaf and cereal crops, and non-crop situations. All imidazolinone herbicides are chiral, containing two enantiomers that derive from the chiral centre of the imidazolinone ring. The inhibitory activity of the R(+) enantiomer is nearly eight times greater than that of the S(-) enantiomer. The use of imidazolinone herbicides has increased in recent years in Australia owing to increased popularity of pulses and the introduction of imidazolinone-tolerant canola and wheat. Concerns have been raised about the potential carry over damage to the subsequent crops grown in rotation with legumes and herbicide tolerant crops. -
Efficacy of Imazapic/Imazapyr and Other Herbicides in Mixtures for The
Efficacy of imazapic/imazapyr and other herbicides in mixtures for the control of Digitaria insularis prior to soybean sowing Efectividad de imazapic/imazapyr y otros herbicidas en mezclas para el control de Digitaria insularis en pre-siembra de soya Alfredo Junior Paiola Albrecht1, Leandro Paiola Albrecht1, André Felipe Moreira Silva²*, Romulo Augusto Ramos³, Everson Pedro Zeny³, Juliano Bortoluzzi Lorenzetti4, Maikon Tiago Yamada Danilussi4, and Arthur Arrobas Martins Barroso4 ABSTRACT RESUMEN Herbicide mixtures, use of multiple sites of action, and other Las mezclas entre herbicidas, el uso de múltiples sitios de acción weed management practices are necessary to avoid cases of y otras prácticas de manejo de malezas son necesarias para biotype resistance. The aim of this study was to evaluate the evitar otros casos de resistencia de biotipos. El objetivo de este efficiency of imazapic/imazapyr and other herbicides in mix- estudio fue evaluar la eficiencia de imazapic/imazapyr y otros tures to control Digitaria insularis at burndown before soybean herbicidas en mezclas para controlar Digitaria insularis en la sowing. This field research was conducted in Umuarama, State desecación antes de la siembra de soya. Esta investigación de of Parana (PR), Brazil, in the 2018/19 soybean season. The ex- campo se realizó en Umuarama, Estado de Paraná (PR), Brasil, periment was conducted in a randomized block experimental en la cosecha de soya de 2018/19. El experimento se realizó en design with four replicates and 11 treatments composed of the un diseño experimental de bloques al azar, con cuatro repe- application of glyphosate, clethodim, haloxyfop, imazapic/ ticiones y 11 tratamientos, compuestos por la aplicación de imazapyr, glufosinate, 2,4-dichlorophenoxyacetic acid (2,4-D), glifosato, cletodim, haloxifop, imazapic/imazapir, glufosinato, dicamba, triclopyr, and saflufenacil, in mixtures. -
Weed Management with Diclosulam in Peanut (Arachis Hypogaea)1
Weed Technology. 2002. Volume 16:724–730 Weed Management with Diclosulam in Peanut (Arachis hypogaea)1 ANDREW J. PRICE, JOHN W. WILCUT, and CHARLES W. SWANN2 Abstract: Field experiments were conducted at three locations in North Carolina in 1998 and 1999 and one location in Virginia in 1998 to evaluate weed management systems in peanut. Treatments consisted of diclosulam alone preemergence (PRE), or diclosulam plus metolachlor PRE alone or followed by (fb) bentazon plus acifluorfen postemergence (POST). These systems were also com pared with commercial standards of metolachlor PRE fb bentazon plus acifluorfen POST or imazapic POST. Our data indicate that diclosulam PRE plus metolachlor PRE in conventional tillage peanut production usually controlled common lambsquarters, common ragweed, prickly sida, and entireleaf morningglory. But control of spurred anoda, goosegrass, ivyleaf morningglory, large crabgrass, and pitted morningglory by this system was inconsistent and may require additional POST herbicide treatments. Systems that included diclosulam plus metolachlor PRE consistently provided high yields and net returns. Nomenclature: Acifluorfen, bentazon, diclosulam, imazapic, metolachlor; common lambsquarters, Chenopodium album L. #3 CHEAL; common ragweed, Ambrosia artemisiifolia L. # AMBEL; enti releaf morningglory, Ipomoea hederacea var. integruiscula Grey # IPOHG; goosegrass, Eleusine indica (L.) Gaertn. # ELEIN; ivyleaf morningglory, Ipomoea hederacea (L.) Jacq # IPOHE; large crabgrass, Digitaria sanguinalis L. Scop. # DIGSA; pitted morningglory, Ipomoea lacunosa L. # IPOLA; prickly sida, Sida spinosa L. # SIDSP; spurred anoda, Anoda cristata L. # ANVCR; peanut, Arachis hypogaea L. ‘NC 10C’, ‘NC 12C’. Additional index words: Economic analysis. Abbreviations: fb, followed by; POST, postemergence; PPI, preplant incorporated; PRE, preemer gence. INTRODUCTION Wilcut and Swann 1990; Wilcut et al. -
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 -
Weed Control in Winter Crops 2019
Weed control in winter crops 2019 NSW DPI MANAGEMENT GUIDE Greg Brooke and Colin McMaster www.dpi.nsw.gov.au New Axial Xtra. Local trial results show the new AXIAL XTRA formulation with an advanced built in adjuvant, delivers improved activity on Wild Oats, Phalaris and Ryegrass, with the same trusted crop safety. Speak to your advisor about AXIAL XTRA today. UP TO 30% CASHBACK agriclime.syngenta.com.au Partner of Visit syngenta.com.au Syngenta Australia Pty Ltd, Level 1, 2-4 Lyonpark Road, Macquarie Park NSW 2113. ABN 33 002 933 717. ® Registered trademark of Syngenta Group Company. *A maximum of 30% cash back may be payable. Please visit agriclime.syngenta.com for full terms and conditions. Axial Xtra is a registered trademark of a Syngenta Group Company. AD 19-038. Weed control in winter crops 2019 Greg Brooke Colin McMaster Research and Development Research and Development Agronomist, Trangie Agronomist, Orange NSW Department of Primary Industries NSW Department of Primary Industries [email protected] [email protected] More consistent control than Trifluralin + Triallate, at less than $30 a hectare. Consistent ryegrass control at a good honest price. To find out more, talk to your local reseller or visit www.TheHonestAgronomist.com.au UP TO 30% CASHBACK agriclime.syngenta.com.au Partner of Visit syngenta.com.au Syngenta Australia Pty Ltd, Level 1, 2-4 Lyonpark Road, Macquarie Park NSW 2113. ABN 33 002 933 717. ® Registered trademark of Syngenta Group Company. *A maximum of 30% cash back may be payable. Please visit agriclime.syngenta.com for full terms and conditions. -
Comparison of Imazapyr and Imazamox for Control of Parrotfeather (Myriophyllum Aquaticum (Vell.) Verdc.)
J. Aquat. Plant Manage. 45: 132-136 Comparison of Imazapyr and Imazamox for Control of Parrotfeather (Myriophyllum aquaticum (Vell.) Verdc.) RYAN M. WERSAL1 AND JOHN D. MADSEN1,2 INTRODUCTION techniques (Moreira et al. 1999). To date, chemical control has been the most effective method for controlling infesta- Parrotfeather (Myriophyllum aquaticum (Vell. Verdc) is an in- tions of M. aquaticum. Contact herbicides such as diquat vasive aquatic plant to the United States that is native to South (6,7-dihydrodipyrido (1,2-a:2’,1’-c) pyrazinedium dibro- America. Myriophyllum aquaticum is described as “stout, stems mide) and endothall (7-oxabicyclo (2.2.1) heptane-2,3-dicar- moderately elongate, partially submersed but with portions of boxylic acid) have been evaluated with mixed results leafy branches emersed (Godfrey and Wooten 1981). Emer- (Moreira et al. 1999, Westerdahl and Getsinger 1988). Con- gent leaves are whorled, stiff, usually with 20 or more linear fil- tact herbicides are typically effective for short-term control, iform divisions, appearing feather-like and grayish green. but significant regrowth of M. aquaticum typically occurs and Submersed shoots are comprised of whorls of four to six fila- multiple applications are necessary (Moreira et al. 1999). mentous, pectinate, red or orange, leaves arising from each Therefore, the use of a systemic herbicide may be more ef- node. Flowers are all pistillate, borne in the axils of unreduced fective in controlling this species. leaves (Godfrey and Wooten 1981). Myriophyllum aquaticum is Imazapyr (2-[4,5-dihydro-4-methyl-4-(1-methylethyl)5-oxo- dioecious, however only pistillate plants are found outside of 1H-imazol-2-yl]-3-pyridinecarboxylic acid) is a systemic herbi- its native range (Sutton 1985). -
Imazapyr Human Health and Ecological Risk Assessment FINAL REPORT
SERA TR-052-29-03a Imazapyr Human Health and Ecological Risk Assessment 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-11-0012 SERA Internal Task No. 52-29 Submitted by: Patrick R. Durkin Syracuse Environmental Research Associates, Inc. 8125 Solomon Seal Manlius, New York 13104 E-Mail: [email protected] Home Page: www.sera-inc.com December 16, 2011 Table of Contents LIST OF FIGURES ...................................................................................................................... vii LIST OF TABLES ........................................................................................................................ vii LIST OF APPENDICES ............................................................................................................... vii ACRONYMS, ABBREVIATIONS, AND SYMBOLS .............................................................. viii COMMON UNIT CONVERSIONS AND ABBREVIATIONS .................................................... x CONVERSION OF SCIENTIFIC NOTATION ........................................................................... xi EXECUTIVE SUMMARY .......................................................................................................... xii 1. INTRODUCTION ...................................................................................................................... 1 1.1. Chemical Specific Information -
List of Herbicide Groups
List of herbicides Group Scientific name Trade name clodinafop (Topik®), cyhalofop (Barnstorm®), diclofop (Cheetah® Gold*, Decision®*, Hoegrass®), fenoxaprop (Cheetah® Gold* , Wildcat®), A Aryloxyphenoxypropionates fluazifop (Fusilade®, Fusion®*), haloxyfop (Verdict®), propaquizafop (Shogun®), quizalofop (Targa®) butroxydim (Falcon®, Fusion®*), clethodim (Select®), profoxydim A Cyclohexanediones (Aura®), sethoxydim (Cheetah® Gold*, Decision®*), tralkoxydim (Achieve®) A Phenylpyrazoles pinoxaden (Axial®) azimsulfuron (Gulliver®), bensulfuron (Londax®), chlorsulfuron (Glean®), ethoxysulfuron (Hero®), foramsulfuron (Tribute®), halosulfuron (Sempra®), iodosulfuron (Hussar®), mesosulfuron (Atlantis®), metsulfuron (Ally®, Harmony®* M, Stinger®*, Trounce®*, B Sulfonylureas Ultimate Brushweed®* Herbicide), prosulfuron (Casper®*), rimsulfuron (Titus®), sulfometuron (Oust®, Eucmix Pre Plant®*), sulfosulfuron (Monza®), thifensulfuron (Harmony®* M), triasulfuron, (Logran®, Logran® B Power®*), tribenuron (Express®), trifloxysulfuron (Envoke®, Krismat®*) florasulam (Paradigm®*, Vortex®*, X-Pand®*), flumetsulam B Triazolopyrimidines (Broadstrike®), metosulam (Eclipse®), pyroxsulam (Crusader®Rexade®*) imazamox (Intervix®*, Raptor®,), imazapic (Bobcat I-Maxx®*, Flame®, Midas®*, OnDuty®*), imazapyr (Arsenal Xpress®*, Intervix®*, B Imidazolinones Lightning®*, Midas®*, OnDuty®*), imazethapyr (Lightning®*, Spinnaker®) B Pyrimidinylthiobenzoates bispyribac (Nominee®), pyrithiobac (Staple®) C Amides: propanil (Stam®) C Benzothiadiazinones: bentazone (Basagran®, -
Pesticide Reference Values Comparison Study
Is Protecting Aquatic Life from Pesticides Sufficient to Ensure Human Health Protection in Sources of Drinking Water? Kelly D. Moran, Ph.D., TDC Environmental, LLC Bonny Starr, P.E., Starr Consulting October 1, 2018 Abstract California water and pesticides regulators have long operated under the informal assumption that programs to protect aquatic life from currently used pesticides will also ensure the safety of surface water drinKing water sources. This paper examines the scientific validity of this assumption for the agricultural pesticides in California’s Central Valley by comparing water quality regulatory values and benchmarks (“reference values”) for human health with those for aquatic life. Because numeric water quality criteria and other numeric regulatory values established for water quality protection exist for only a handful of currently used pesticides, the comparison relies heavily on US EPA pesticides human health and aquatic life benchmarks. For acute endpoints, both human health and aquatic life reference values typically use a one-day exposure time frame, but chronic endpoint exposure periods differ, with aquatic life exposure periods (4 to 60 days) usually shorter than human health exposure periods (annual). The evaluation looKed in detail at 301 agricultural pesticides with human health reference values. Of these 301 pesticides, only 46% had aquatic life reference values that were equal to or lower than the human health reference value. For 54% of these pesticides, either no aquatic life reference value existed or the aquatic life reference value was higher than the human health reference value. In these cases, aquatic life protection actions would not suffice to protect human health. -
Horticultural Weed Control Report
Horticultural Weed Control Report 2003 and 2004 Web downloads Ed Peachey, Senior Research Assistant Horticultural Weed Science Phone: 541-737-3152 [email protected] Ray D. William, Extension Horticultural Weed Specialist Phone: 541-737-5441 Williamr@ science.oregonstate.edu Lee Ann Julson Extension Secretary Not intended or authorized for publication Data contained in this report are compiled annually as an aide to complete minor crop registrations for horticultural crops and to communicate our results to colleagues and funding sources. Data are neither intended nor authorized for publication. Information and interpretation cannot be construed as recommendations for application of any herbicide or weed control practice mentioned in this report. Contributors Susan Aldrich-Markham Yamhill Co. Extension, McMinnville Chris Boerboom Univ. of Wisconsin, Madison Glenn Fisher Extension Entomologist, OSU Diane Kaufman NWREC, Aurora, OR Gina Koskela NWREC, Aurora, OR Judy Kowalski NWREC, Aurora, OR Robin Ludy Research Assistant, Botany & Plant Pathology Dept., OSU Carol Smith Professor of Weed Science, Crop and Soil Science Dept., OSU Dan McGrath Marion County Extension, Salem, OR Bob McReynolds Dist. Ext. Agent, NWREC, Aurora, OR James R. Myers Baggett-Frazier Professor of Vegetable Breeding and Genetics, Horticulture Dept., OSU Cindy Ocamb Pathologist, Botany and Plant Pathology Mary Powelson Botany and Plant Pathology, OSU David Rupp Bioresource Engineering, OSU John Selker Bioresource Engineering, OSU Alex Stone Horticulture, OSU Jon Umble Graduate Student, Entomology Ray D. William Extension Horticultural Weed Specialist, OSU Special thanks to these cooperators and facilitators Jim Ammon, Wilbur Ellis, Jefferson Corey Antrim, Antrim Farms Jim Belden, Stayton Roger Fitts, Independence Randy Hopson, OSU Vegetable Res.