H E R B I C I D E F a C T S H E E T 2,4-D (See Figure 1) Is a Chloro
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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. -
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. -
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. -
12 Chemical Fact Sheets
1212 ChemicalChemical factfact sheetssheets A conceptual framework for Introduction implementing the Guidelines (Chapter 1) (Chapter 2) he background docudocu-- ments referred to in FRAMEWORK FOR SAFE DRINKING-WATER SUPPORTING Tments referred to in INFORMATION thisthis chapterchapter (as the princi-princi- Health-based targets Public health context Microbial aspects pal reference for each fact (Chapter 3) and health outcome (Chapters 7 and 11) sheet) may be found on Water safety plans Chemical aspects (Chapter 4) (Chapters 8 and 12) thethe Water, Sanitation, HyHy-- System Management and Radiological Monitoring giene and Health web site assessment communication aspects at http://www.who.int/ (Chapter 9) Acceptability Surveillance water_sanitation_health/ aspects (Chapter 5) dwq/chemicals/en/indewater-quality/guidelines/x. (Chapter 10) htmlchemicals/en/. A complete. A complete list of rlist eferences of references cited citedin this in Application of the Guidelines in specic circumstances chapter,this chapter, including including the (Chapter 6) background documents Climate change, Emergencies, Rainwater harvesting, Desalination forfor each cchemical, hemical, is pro-pro- systems, Travellers, Planes and vided in Annex 22.. ships, etc. 12.1 Chemical contaminants in drinking-water Acrylamide Residual acrylamideacrylamide monomermonomer occursoccurs inin polyacrylamidepolyacrylamide coagulantscoagulants used used in in thethe treattreat-- ment of drinking-water. In general, thethe maximummaximum authorizedauthorized dosedose ofof polymerpolymer isis 11 mg/l. mg/l. At a monomer content of 0.05%, this corresponds to a maximum theoretical concen-- trationtration ofof 0.5 µg/l of the monomer in water.water. Practical concentrations maymay bebe lowerlower byby aa factor factor of 2–3. This applies applies to to thethe anionic anionic and and non-ionic non-ionic polyacrylamides, polyacrylamides, but but residual residual levelslevels fromfrom cationic polyacrylamides maymay bebe higher.higher. -
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®, -
Mecoprop Final V3.1
Science Group report NC/03/12 Attenuation of mecoprop in the subsurface Environment Agency Science Group: Air, Land & Water The Environment Agency is the leading public body protecting and improving the environment in England and Wales. It’s our job to make sure that air, land and water are looked after by everyone in today’s society, so that tomorrow’s generations inherit a cleaner, healthier world. Our work includes tackling flooding and pollution incidents, reducing industry’s impacts on the environment, cleaning up rivers, coastal waters and contaminated land, and improving wildlife habitats. Authors: Published by: J. Thrasher1, P. Morgan2 & S. R. Buss2. 1 Jacobs Gibb, Gibb House, London Road, Reading, RG6 1BL. Environment Agency 2 Rio House Environmental Simulations International Ltd, Priory House, Priory Road, Shrewsbury, SY1 1RU. Waterside Drive, Aztec West Almondsbury, Bristol, BS32 4UD Statement of use: Tel: 01454 624400 Fax: 01454 624409 This report presents a literature review of mecoprop attenuation processes in the subsurface environment. It IC Code: BHST includes summarised rates for biodegradation and sorption reactions from field and laboratory experiments. The © Environment Agency, March 2004 presented data may be used for initial risk-screening, but site-specific data collection is expected where the output All rights reserved. This document may be reproduced with from an initial assessment of pollution risks is indicates that prior permission of the Environment Agency. it is sensitive to mecoprop attenuation parameters. This report is printed on Cyclus Print, a 100% recycled stock, which is 100% post consumer waste and is totally chlorine free. Environment Agency project manager: Water used is treated and in most cases returned to source in Jonathan Smith, Science Group: Air, Land & Water better condition than removed. -
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. -
Spatial Variability of Atrazine and Metolachlor Dissipation on Dryland No-Tillage Crop Fields in Colorado
TECHNICAL REPORTS: ORGANICTECHNICAL COMPOUNDS REPORTS IN THE ENVIRONMENT Spatial Variability of Atrazine and Metolachlor Dissipation on Dryland No-tillage Crop Fields in Colorado Melissa Bridges* Colorado State University W. Brien Henry and Dale L. Shaner USDA-ARS R. Khosla, Phil Westra, and Robin Reich Colorado State University An area of interest in precision farming is variable-rate ite-specific management of a crop fi eld requires that the application of herbicides to optimize herbicide use effi ciency Svariability associated with factors that limit productivity and minimize negative off -site and non-target eff ects. Site- be spatially characterized. If such factors vary across a fi eld specifi c weed management based on fi eld scale management zones derived from soil characteristics known to aff ect soil- at an agronomically signifi cant level, the use of site-specifi c applied herbicide effi cacy could alleviate challenges posed by or precision farming techniques may be benefi cial. One area post-emergence precision weed management. Two commonly of interest in precision farming is variable-rate application of used soil-applied herbicides in dryland corn (Zea mays L.) herbicides to optimize herbicide use effi ciency and minimize production are atrazine and metolachlor. Accelerated dissipation negative off -site and non-target eff ects. of atrazine has been discovered recently in irrigated corn fi elds in eastern Colorado. Th e objectives of this study were (i) to Th e conventional approach to herbicide application is to treat compare the rates of dissipation of atrazine and metolachlor an entire fi eld uniformly. Recent studies have suggested that across diff erent soil zones from three dryland no-tillage fi elds herbicides might be applied diff erentially according to spatially under laboratory incubation conditions and (ii) to determine varying soil properties (Jaynes et al., 1995; Gaston et al., 2001; if rapid dissipation of atrazine and/or metolachlor occurred Williams et al., 2002). -
Effects of Various Environmental Conditions on the Growth of Amaranthus Patulus Bertol
agronomy Article Effects of Various Environmental Conditions on the Growth of Amaranthus patulus Bertol. and Changes of Herbicide Efficacy Caused by Increasing Temperatures Hyun-Hwa Park 1, Do-Jin Lee 2 and Yong-In Kuk 1,* 1 Department of Bio-Oriental Medicine Resources, Sunchon National University, Suncheon 57922, Korea; [email protected] 2 Department of Agricultural Education, Sunchon National University, Suncheon 57922, Korea; [email protected] * Correspondence: [email protected] Abstract: Understanding the effects of climate change on weed growth and herbicide activity is important for optimizing herbicide applications for effective weed control in the future. Therefore, this study examined how climate change affects the growth of Amaranthus patulus and the efficacy of soil and foliar herbicides at different temperatures. Although the control values for A. patulus differed between herbicides and temperature, the control values increased with increasing time after the herbicide treatments. Under growth conditions in which the temperature remained constant, the efficacy of soil-applied herbicides, ethalfluralin, metolachlor, linuron, and alachlor, on A. patulus was highest when the weeds were grown at high temperature. In particular, 100% control values of A. patulus were achieved in response to metolachlor treatments at the total recommended dosage in growth chambers at 35 ◦C. The efficacy of foliar herbicides, glufosinate-ammonium, bentazone, Citation: Park, H.-H.; Lee, D.-J.; Kuk, and mecoprop, on A. patulus was also highest when the plant was grown at high temperature, Y.-I. Effects of Various Environmental except for glyphosate isopropylamine, which had similar efficacy rates regardless of the temperature. Conditions on the Growth of A. -
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.