HERBICIDE INJURIES to TREES—SYMPTOMS and SOLUTIONS by James R
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Evolution of Resistance to Auxinic Herbicides: Historical Perspectives, Mechanisms of Resistance, and Implications for Broadleaf Weed Management in Agronomic Crops J
Weed Science 2011 59:445–457 Evolution of Resistance to Auxinic Herbicides: Historical Perspectives, Mechanisms of Resistance, and Implications for Broadleaf Weed Management in Agronomic Crops J. Mithila, J. Christopher Hall, William G. Johnson, Kevin B. Kelley, and Dean E. Riechers* Auxinic herbicides are widely used for control of broadleaf weeds in cereal crops and turfgrass. These herbicides are structurally similar to the natural plant hormone auxin, and induce several of the same physiological and biochemical responses at low concentrations. After several decades of research to understand the auxin signal transduction pathway, the receptors for auxin binding and resultant biochemical and physiological responses have recently been discovered in plants. However, the precise mode of action for the auxinic herbicides is not completely understood despite their extensive use in agriculture for over six decades. Auxinic herbicide-resistant weed biotypes offer excellent model species for uncovering the mode of action as well as resistance to these compounds. Compared with other herbicide families, the incidence of resistance to auxinic herbicides is relatively low, with only 29 auxinic herbicide-resistant weed species discovered to date. The relatively low incidence of resistance to auxinic herbicides has been attributed to the presence of rare alleles imparting resistance in natural weed populations, the potential for fitness penalties due to mutations conferring resistance in weeds, and the complex mode of action of auxinic herbicides in sensitive dicot plants. This review discusses recent advances in the auxin signal transduction pathway and its relation to auxinic herbicide mode of action. Furthermore, comprehensive information about the genetics and inheritance of auxinic herbicide resistance and case studies examining mechanisms of resistance in auxinic herbicide-resistant broadleaf weed biotypes are provided. -
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. -
Please Use Caution When Applying Herbicides Near Wine Grapes
Please Use Caution When Applying Herbicides Near Wine Grapes Phenoxy herbicides are very damaging to grapevines Grapevines are extremely sensitive to the application of certain herbicides commonly used by farmers and homeowners, especially phenoxy herbicides. Phenoxy herbicides include 2,4-D, MCPA, Crossbow, Banvel, Garlon, Weed-B-Gone, and Brush Killer, among others. The active ingredient of phenoxy-type herbicides may be listed on the label in “weed and feed” and brush control products for use in home landscaping as 2,4-dichlorophenoxy- acetic acid (2,4-D), 2-methyl-4-chlorophenoxyacetic acid, triclopyr, or dicamba. Sensitivity to phenoxy herbicides exists throughout the grapevine's growing season (mid-March through October). Grapevines are most vulnerable from the early growing season through the bloom and fruit set period (mid-March through June). Phenoxy herbicides do not require a pesticide license for purchase in Oregon and are readily available from home improvement stores, garden centers, retail nurseries, etc. This family of herbicides is very effective and economical for controlling broadleaf weeds. These herbicides are commonly used on a variety of sites such as lawns, golf courses, rights-of-way and agricultural fields and by homeowners. Two forms of spray drift can damage grapevines Drift of spray droplets: Small particles can move with the wind, land on grapes, and be absorbed into the grapevines through the cuticle on the leaf. The smaller the droplet, the further it will travel. Vapor drift: Volatile herbicides may produce vapors that are carried several miles from the target area. Herbicide particles or vapors may be moved from the application site by wind, shifting air currents, climatic inversions or using high pressures when spraying. -
AP-42, CH 9.2.2: Pesticide Application
9.2.2PesticideApplication 9.2.2.1General1-2 Pesticidesaresubstancesormixturesusedtocontrolplantandanimallifeforthepurposesof increasingandimprovingagriculturalproduction,protectingpublichealthfrompest-bornediseaseand discomfort,reducingpropertydamagecausedbypests,andimprovingtheaestheticqualityofoutdoor orindoorsurroundings.Pesticidesareusedwidelyinagriculture,byhomeowners,byindustry,andby governmentagencies.Thelargestusageofchemicalswithpesticidalactivity,byweightof"active ingredient"(AI),isinagriculture.Agriculturalpesticidesareusedforcost-effectivecontrolofweeds, insects,mites,fungi,nematodes,andotherthreatstotheyield,quality,orsafetyoffood.Theannual U.S.usageofpesticideAIs(i.e.,insecticides,herbicides,andfungicides)isover800millionpounds. AiremissionsfrompesticideusearisebecauseofthevolatilenatureofmanyAIs,solvents, andotheradditivesusedinformulations,andofthedustynatureofsomeformulations.Mostmodern pesticidesareorganiccompounds.EmissionscanresultdirectlyduringapplicationorastheAIor solventvolatilizesovertimefromsoilandvegetation.Thisdiscussionwillfocusonemissionfactors forvolatilization.Thereareinsufficientdataavailableonparticulateemissionstopermitemission factordevelopment. 9.2.2.2ProcessDescription3-6 ApplicationMethods- Pesticideapplicationmethodsvaryaccordingtothetargetpestandtothecroporothervalue tobeprotected.Insomecases,thepesticideisapplieddirectlytothepest,andinotherstothehost plant.Instillothers,itisusedonthesoilorinanenclosedairspace.Pesticidemanufacturershave developedvariousformulationsofAIstomeetboththepestcontrolneedsandthepreferred -
Redox Imbalance Caused by Pesticides: a Review of OPENTOX-Related Research
Marjanović Čermak AM, et al. Redox imbalance caused by pesticides Arh Hig Rada Toksikol 2018;69:126-134 126 Review DOI: 10.2478/aiht-2018-69-3105 Redox imbalance caused by pesticides: a review of OPENTOX-related research Ana Marija Marjanović Čermak, Ivan Pavičić, and Davor Želježić Institute for Medical Research and Occupational Health, Zagreb, Croatia [Received in February 2018; Similarity Check in February 2018; Accepted in May 2018] Pesticides are a highly diverse group of compounds and the most important chemical stressors in the environment. Mechanisms that could explain pesticide toxicity are constantly being studied and their interactions at the cellular level are often observed in well-controlled in vitro studies. Several pesticide groups have been found to impair the redox balance in the cell, but the mechanisms leading to oxidative stress for certain pesticides are only partly understood. As our scientific project “Organic pollutants in environment – markers and biomarkers of toxicity (OPENTOX)” is dedicated to studying toxic effects of selected insecticides and herbicides, this review is focused on reporting the knowledge regarding oxidative stress-related phenomena at the cellular level. We wanted to single out the most important facts relevant to the evaluation of our own findings from studies conducted onin vitro cell models. KEY WORDS: antioxidants; apoptosis; glyphosate; in vitro; neonicotinoids; organophosphates; oxidative stress; pyrethroids; reactive oxygen species Over the years, population growth and changes in food (HrZZ), is dedicated to studying the toxic effects of two consumption patterns have challenged agricultural major pesticide classes with three subgroups each: (A) production to meet the demand for food and quality insecticides (organophosphates, neonicotinoids, and standards. -
US Environmental Protection Agency Office of Pesticide Programs
US Environmental Protection Agency Office of Pesticide Programs Reregistration Eligibility Decision for Prometon March 25, 2008 United States Prevention, Pesticides EPA 738-R-08-004 Environmental Protection and Toxic Substances Agency (7508P) Reregistration Eligibility Decision for Prometon TABLE OF CONTENTS GLOSSARY OF TERMS AND ABBREVIATIONS............................................................................... 4 I. INTRODUCTION.............................................................................................................................. 5 II. CHEMICAL OVERVIEW................................................................................................................ 6 A. REGULATORY HISTORY ................................................................................................................... 6 B. CHEMICAL IDENTIFICATION............................................................................................................. 6 C. USE PROFILE .................................................................................................................................... 7 D. ESTIMATED USAGE OF PESTICIDE.................................................................................................... 8 III. SUMMARY OF PROMETON RISK ASSESSMENTS............................................................. 9 A. HUMAN HEALTH RISK ASSESSMENT ............................................................................................... 9 1. Toxicity of Prometon.................................................................................................................. -
Pesticide Contamination Prevention Program Report A.R.S
Pesticide Contamination Prevention Program Report A.R.S. 49-303.C § The Arizona Pesticide Contamination Prevention Program was established by the Environmental Quality Act of 1986. The major objective of the program is to prevent or mitigate groundwater pollution by agricultural pesticides. The program is composed of the following four major components: 1) Product chemistry and environmental fate review – Prior to registering an agricultural-use pesticide with the Arizona Department of Agriculture (ADA), applicants must submit product chemistry and environmental fate data of the associated active ingredient to ADEQ for review and approval. The information is used to determine the potential of the active ingredient to leach to groundwater, and generate the Arizona Groundwater Protection List (GWPL). 2) Groundwater Protection List – The GWPL is a list of agricultural pesticides in use in Arizona and their active ingredients that have the potential to pollute groundwater, based on product chemistry and environmental fate data and groundwater monitoring of the active ingredient(s). 3) Environmental monitoring – ADEQ, in cooperation with the ADA, monitors groundwater and soils in agricultural areas throughout the state for the presence of agricultural-use pesticide active ingredients on the GWPL. 4) Compilation of data – ADEQ collects and reports product use information for agricultural pesticides applied to the soil on the GWPL. Results of pesticide monitoring for ground-water wells are evaluated and stored in the Water Quality Division’s groundwater database. This report which covers calendar year 2011 is in fulfillment of a requirement pursuant to A.R.S. § 49- 303.C that requires ADEQ to report the following information to the Legislature annually: 1) A list of agricultural-use pesticide active ingredient for which there is a groundwater protection data gap (A.R.S. -
AP-42, Vol. 1, Final Background Document for Pesticide Application
Emission Factor Documentation for AP-42 Section 9.2.2 Pesticide Application Final Report For U.S. Environmental Protection Agency Office of Air Quality Planning and Standards Emission Inventory Branch EPA Contract No. 68-D2-0159 Work Assignment No. I-08 MRI Project No. 4601-08 September 1994 Emission Factor Documentation for AP-42 Section 9.2.2 Pesticide Application Final Report For U.S. Environmental Protection Agency Office of Air Quality Planning and Standards Emission Inventory Branch Research Triangle Park, NC 27711 Attn: Mr. Dallas Safriet (MD-14) Emission Factor and Methodology EPA Contract No. 68-D2-0159 Work Assignment No. I-08 MRI Project No. 4601-08 September 1994 NOTICE The information in this document has been funded wholly or in part by the United States Environmental Protection Agency under Contract No. 68-D2-0159 to Midwest Research Institute. It has been subjected to the Agency's peer and administrative review, and it has been approved for publication as an EPA document. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. iii iv PREFACE This report was prepared by Midwest Research Institute (MRI) for the Office of Air Quality Planning and Standards (OAQPS), U.S. Environmental Protection Agency (EPA), under Contract No. 68-D2-0159, Assignment No. 005 and I-08. Mr. Dallas Safriet was the EPA work assignment manager for this project. Approved for: MIDWEST RESEARCH INSTITUTE Roy M. Neulicht Program Manager Environmental Engineering Department Jeff Shular Director, Environmental Engineering Department September 29, 1994 v vi CONTENTS LIST OF FIGURES ................................................ viii LIST OF TABLES ................................................ -
INSECT, WEED, Anddisease CONTROL in TURFGRASS
SC-039 5/17 WEED,INSECT, and DISEASE CONTROL in TURFGRASS 2017–18 WEED, INSECT, and DISEASE CONTROL in TURFGRASS Editor Casey Reynolds, Assistant Professor and Extension Turfgrass Specialist Authors Casey Reynolds, Assistant Professor and Extension Turfgrass Specialist Matt Elmore, Assistant Professor and Extension Turfgrass Specialist Young-Ki Jo, Associate Professor and Extension Turfgrass Specialist Diane Silcox Reynolds, Post-doctoral Research Associate, Entomology AggieTurf: http://aggieturf.tamu.edu Contents Introduction . 1 Herbicide Mode of Action (MOA) classification . 3 Herbicides for general control of grassy and broadleaf weeds . 4 Preemergence herbicides for grassy and broadleaf weeds . 4 Selective postemergence herbicides . 9 Synthetic auxin postemergence herbicides for broadleaf weeds . 19 Product formulations containing synthetic auxin herbicides . 21 Nonsynthetic auxin postemergence herbicides for broadleaf weeds . 23 Nonselective herbicides for general weed control . 24 Herbicides for commonly occurring weeds . 25 Crabgrass (Digitaria spp ). 25 Goosegrass (Eleusine indica) . 27 Sandbur (Cenchrus spp ). 30 Annual bluegrass (Poa annua L ). 33 Dallisgrass (Paspalum dilatatum Poir ). 39 WEEDS Bermudagrass (Cynodon spp ). 41 Nutsedge (Cyperus spp ). and kyllinga (Kyllinga spp ). 43 Khakiweed and mat chafflower (Alternanthera spp ). 46 Herbicides containing sulfentrazone . 47 Herbicides containing quinclorac . 48 Turfgrass tolerance to postemergence herbicides . 49 Plant growth regulators . 51 Insect pests in turfgrasses . 53 Insecticide Mode of Action (MOA) classification . 55 Insecticides registered for use in turfgrasses . 56 Ants . 56 Armyworms . 58 Billbugs . 61 Black turfgrass ataenius . 63 Chinch bugs . 66 Cutworms . 69 Green June beetles . 72 Mealybugs . 74 Mites . 75 INSECTS Mole crickets . 76 Red imported fire ants . 79 Sod webworms . 81 White grubs . 84 Diseases in Texas turfgrasses . 86 Fungicide Mode of Action (MOA) classification . -
PESTICIDES Criteria for a Recommended Standard
CRITERIA FOR A RECOMMENDED STANDARD OCCUPATIONAL EXPOSURE DURING THE MANUFACTURE AND FORMULATION OF PESTICIDES criteria for a recommended standard... OCCUPATIONAL EXPOSURE DURING THE MANUFACTURE AND FORMULATION OF PESTICIDES * U.S. DEPARTMENT OF HEALTH, EDUCATION, AND WELFARE Public Health Service Center for Disease Control National Institute for Occupational Safety and Health July 1978 For sale by the Superintendent of Documents, U.S. Government Printing Office, Washington, D.C. 20402 DISCLAIMER Mention of company names or products does not constitute endorsement by the National Institute for Occupational Safety and Health. DHEW (NIOSH) Publication No. 78-174 PREFACE The Occupational Safety and Health Act of 1970 emphasizes the need for standards to protect the health and provide for the safety of workers occupationally exposed to an ever-increasing number of potential hazards. The National Institute for Occupational Safety and Health (NIOSH) has implemented a formal system of research, with priorities determined on the basis of specified indices, to provide relevant data from which valid criteria for effective standards can be derived. Recommended standards for occupational exposure, which are the result of this work, are based on the effects of exposure on health. The Secretary of Labor will weigh these recommendations along with other considerations, such as feasibility and means of implementation, in developing regulatory standards. Successive reports will be presented as research and epideiriologic studies are completed and as sampling and analytical methods are developed. Criteria and standards will be reviewed periodically to ensure continuing protection of workers. The contributions to this document on pesticide manufacturing and formulating industries by NIOSH staff members, the review consultants, the reviewer selected by the American Conference of Governmental Industrial Hygienists (ACGIH), other Federal agencies, and by Robert B. -
Recommended Classification of Pesticides by Hazard and Guidelines to Classification 2019 Theinternational Programme on Chemical Safety (IPCS) Was Established in 1980
The WHO Recommended Classi cation of Pesticides by Hazard and Guidelines to Classi cation 2019 cation Hazard of Pesticides by and Guidelines to Classi The WHO Recommended Classi The WHO Recommended Classi cation of Pesticides by Hazard and Guidelines to Classi cation 2019 The WHO Recommended Classification of Pesticides by Hazard and Guidelines to Classification 2019 TheInternational Programme on Chemical Safety (IPCS) was established in 1980. The overall objectives of the IPCS are to establish the scientific basis for assessment of the risk to human health and the environment from exposure to chemicals, through international peer review processes, as a prerequisite for the promotion of chemical safety, and to provide technical assistance in strengthening national capacities for the sound management of chemicals. This publication was developed in the IOMC context. The contents do not necessarily reflect the views or stated policies of individual IOMC Participating Organizations. The Inter-Organization Programme for the Sound Management of Chemicals (IOMC) was established in 1995 following recommendations made by the 1992 UN Conference on Environment and Development to strengthen cooperation and increase international coordination in the field of chemical safety. The Participating Organizations are: FAO, ILO, UNDP, UNEP, UNIDO, UNITAR, WHO, World Bank and OECD. The purpose of the IOMC is to promote coordination of the policies and activities pursued by the Participating Organizations, jointly or separately, to achieve the sound management of chemicals in relation to human health and the environment. WHO recommended classification of pesticides by hazard and guidelines to classification, 2019 edition ISBN 978-92-4-000566-2 (electronic version) ISBN 978-92-4-000567-9 (print version) ISSN 1684-1042 © World Health Organization 2020 Some rights reserved. -
Phenoxy Reference Guide 3
Phenoxy Reference Guide www.nufarm.com.au 3 Contents Introduction 4 Mode of Action 4 Cereal Crop Growth Stages (including Zadok’s guide) 5 A Numerical Cereal Growth Scale – Zadok’s 6 What Phenoxy Where? 6 Common Weeds Controlled 7 Using the Growth Stage of Cereal Crops to Time Herbicide Applications 8 Damage to Cereal Crops from Incorrect Phenoxy Herbicide Applications 9 Salvage Spraying of Winter Crops 10 Cereal Tolerance Guide 11-13 Plant Back Periods for Fallow Seed Bed Preparation 14-15 Spray Grazing 16 Withholding Periods 16 Reducing Off-Target Herbicide Drift 16-19 Herbicide Resistance Management 20 4 Introduction At Nufarm, we are committed to supporting Australian growers Phenoxys were first developed in the USA in the early 1940’s with the highest quality crop protection and weed control and used commercially in 1946. Today they remain amongst products so maximum outputs can be achieved. the world’s most widely used herbicides, providing farmers and other users with broadleaf weed control in a multitude of Our commitment starts with the utilisation of world-leading agricultural and non-agricultural uses. Phenoxys work by manufacturing and environmental control technology. This is disrupting plant cell growth and form a part of the Group I reflected in research and development, container management, herbicides. and the establishment of regional service centres across Australia. Nufarm guarantees its Phenoxy products, which include Nufarm Amicide® 625, Nufarm Estercide® 800, Nufarm LV Nufarm, an Australian company, is a global leader in the Estercide® 600, Nufarm Surpass® 300, Nufarm Buttress®, manufacture, supply and marketing of 'phenoxys', with Baton®, Nufarm LVE MCPA and Nufarm MCPA 500.