Herbicide Resistance Traits in Maize and Soybean: Current Status and Future Outlook
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Roundup Ready Wheat – an Overview Based on Advancements in the Risk Assessment of Genetically Engineered Crops
Roundup Ready Wheat – An Overview Based on Advancements in the Risk Assessment of Genetically Engineered Crops by Doug Gurian-Sherman, Ph.D. Center for Science in the Public Interest 1875 Connecticut Avenue, N.W., Suite 300 Washington, DC 20009-5728 Phone: (202) 332-9110 www.cspinet.org TABLE OF CONTENTS SECTION PAGE Abstract................................................................................................................................. 2 Introduction.......................................................................................................................... 3 Background on the U.S. Regulatory System for GE Crops ............................................. 3 Characterization of the Transgene and Transgenic Protein............................................ 4 Human Safety....................................................................................................................... 6 Allergenicity ...................................................................................................................... 7 Unintended Adverse Effects.............................................................................................. 9 Environmental Issues ........................................................................................................ 11 Resistance Management ................................................................................................. 12 Gene Transfer.............................................................................................................. -
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 -
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®), -
Harness Xtra Herbicide, EPA Registration REPACKAGING LIMITATIONS
ATTENTION: This specimen label is provided for general information only. • This pesticide product may not yet be available or approved for sale or use in your area. • It is your responsibility to follow all Federal, state and local laws and regulations regarding the use of pesticides. • Before using any pesticide, be sure the intended use is approved in your state or locality. • Your state or locality may require additional precautions and instructions for use of this product that are not included here. • Monsanto does not guarantee the completeness or accuracy of this specimen label. The information found in this label may differ from the information found on the product label. You must have the EPA approved labeling with you at the time of use and must read and follow all label directions. • You should not base any use of a similar product on the precautions, instructions for use or other information you find here. • Always follow the precautions and instructions for use on the label of the pesticide you are using. 36021K6-29 3.0 PRECAUTIONARY STATEMENTS RESTRICTED USE PESTICIDE due to ground and surface water concerns. For retail sale to and use only by .1 Hazards to Humans and Domestic Animals Certified Applicators, or persons under their direct supervision and only for those 3 uses covered by the Certified Applicator’s certification. Keep out of reach of children. CAUTION! HARMFUL IF SWALLOWED. HARMFUL IF INHALED. CAUSES MODERATE EYE IRRITATION. ® MAY CAUSE ALLERGIC SKIN REACTION. Avoid contact with skin, eyes, or clothing. Avoid breathing spray mist. Prolonged or frequently repeated skin contact may cause allergic reactions in some individuals. -
Weed Control in Direct-Seeded Field Pea Gregory J
Weed Control in Direct-seeded Field Pea Gregory J. Endres and Blaine G. Schatz Weed control and field pea response to selected soil- and POST-applied herbicides were evaluated in a randomized complete-block design with three replicates. The experiment was conducted on a Heimdahl loam soil with 6.7 pH and 2.9% organic matter at the NDSU Carrington Research Extension Center. Herbicide treatments were applied to 5- by 25-ft plots with a pressurized hand-held plot sprayer at 17 gal/A and 30 psi through 8002 flat-fan nozzles. Fall sulfentrazone treatments were applied October 25, 2004 to a moist soil surface with 47 F, 71% RH, 15% clear sky, and 11 mph wind. On April 28, 2005, inoculated 'Integra' field pea was seeded into standing wheat stubble in 7-inch rows at a rate of 300,000 pure live seeds/A. PRE treatments were applied to a dry soil surface on April 30 with 31 F, 64% RH, 30% clear sky, and 10 mph wind. Rainfall totaled 1.22 inches 8 d following PRE application. The trial area was treated on May 6 with a PRE burn-down application of glyphosate at 0.75 lb ae/A plus ammonium sulfate at 1% v/v. The early POST (EPOST) treatment was applied on May 23 with 73 F, 35% RH, 100% cloudy sky, and 6 mph wind to 2-inch tall field pea, 1- to 2-leaf green and yellow foxtail, 0.5-inch tall common lambsquarters, 0.5-inch tall prostrate and redroot pigweed, and 0.5-inch tall wild buckwheat. -
Agricultural Biotechnology: Benefits of Transgenic Soybeans
AGRICULTURAL BIOTECHNOLOGY: BENEFITS OF TRANSGENIC SOYBEANS Leonard P. Gianessi Janet E. Carpenter April 2000 National Center for Food and Agricultural Policy 1616 P Street, NW, First Floor Washington, DC 20036 Tel: 202-328-5048 Fax: 202-328-5133 [email protected] Preparation of this report was supported financially with a grant from the Rockefeller Foundation TABLE OF CONTENTS 1. Introduction 2. U.S. Soybean Production 3. Soybean Products 4. Soybean Physiology 5. Soybeans – Agronomic Factors 6. Soybean Genetic Improvements A. Introduction B. Reproductive Process C. Artificial Cross Breeding D. Mutation Breeding E. Transgenic Plants 7. Weed Competition – Soybeans 8. Weed Control in Soybeans: 1940’s – 1950’s 9. Herbicides – An Overview 10. Herbicide Use in Soybeans: 1960’s – 1995 A. Introduction B. Historical Overview 1. The Early 1960’s 2. Soil Applied Herbicides 3. Postemergence Herbicides 4. Sulfonylurea/Imidazolinone Herbicides 5. Burndown Herbicides C. Summary of Usage: 1995 11. Transgenic Herbicide Tolerant Soybeans A. Glyphosate – An Overview B. Performance of Roundup Ready Soybeans C. Herbicide Ratings D. Adoption Impacts: 1995 – 1998 1. Herbicide Costs 2. Soybean Yields 3. Returns 4. Other Aggregate Studies 5. Herbicide Treatments 6. Herbicide Use Amounts 7. Other Impacts 12. Summary and Conclusions 13. References Appendix 1: Soybean Processing – A Description 1. Introduction Soybeans and other crops have been improved genetically for many decades through traditional crop breeding – a technique that requires that species be sexually compatible. With the development of biotechnology methods, scientists have the ability to transfer single genes from one living organism into another, regardless of species or sexual compatibility. Varieties that are developed through the transfer of genes between species that are not sexually compatible are referred to as “transgenic.” Transgenic soybean plants have been developed with a gene from a soil bacteria that allows the use of an herbicide that would normally kill soybeans. -
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. -
Appendix C - Wildlife 9/8/2008
INVASIVE PLANT BIOLOGICAL ASSESSMENT Umatilla and Wallowa-Whitman National Forests Appendix C - Wildlife 9/8/2008 APPENDIX C - WILDLIFE C-1 INVASIVE PLANT BIOLOGICAL ASSESSMENT Umatilla and Wallowa-Whitman National Forests Appendix C - Wildlife 9/8/2008 C-2 INVASIVE PLANT BIOLOGICAL ASSESSMENT Umatilla and Wallowa-Whitman National Forests Appendix C - Wildlife 9/8/2008 Appendix C ......................................................................................................................... 1 Wildlife ............................................................................................................................... 1 Exposure Groups for Forest Service Sensitive Wildlife ................................................. 6 Effects of the Alternatives on Sensitive Wildlife ........................................................... 7 Tables C-5 – C-13 Herbicides ................................................................................... 11 Umatilla and Wallowa-Whitman National Forest Herbicide Spray Buffers ................ 12 Aquatics............................................................................................................. 15 Wildlife .............................................................................................................. 15 Worker Health: Based on backpack spray applications. ................................. 15 Public Health: ................................................................................................... 16 Summary of Herbicide Effects to Wildlife -
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 Management—Major Crops
Weed Technology 2010 24:1–5 Weed Management—Major Crops Annual Grass Control in Strip-Tillage Peanut Production with Delayed Applications of Pendimethalin W. Carroll Johnson, III, Eric P. Prostko, and Benjamin G. Mullinix, Jr.* In strip-tillage peanut production, situations occur when dinitroaniline herbicides are not applied in a timely manner. In these cases, dinitroaniline herbicides would be applied days or weeks after seeding. However, there is no information that documents the effects of delayed applications on weed control. Trials were conducted in 2004, 2005, and 2007 in Georgia to determine the weed control efficacy of delayed applications of pendimethalin in strip-tillage peanut production. Treatments included seven timings of pendimethalin application and three pendimethalin-containing herbicide combinations. Timings of application were immediately after seeding (PRE), vegetative emergence of peanut (VE), 1 wk after VE (VE+1wk), VE+2wk, VE+3wk, VE+4wk, and a nontreated control. Pendimethalin containing herbicide programs included pendimethalin plus paraquat, pendimethalin plus imazapic, and pendimethalin alone. Among the possible treatment combinations was a current producer standard timing for nonpendimethalin weed control programs in peanut, which was either imazapic or paraquat alone applied VE+3wk. Pendimethalin alone did not effectively control Texas millet regardless of time of application (69 to 77%), whereas southern crabgrass was controlled by pendimethalin alone PRE (87%). Delayed applications of pendimethalin controlled Texas millet and southern crabgrass when combined with either paraquat or imazapic, with imazapic being the preferred combination due to better efficacy on southern crabgrass than paraquat at most delayed applications. Peanut yield was improved when any of the herbicide combinations were applied PRE compared to later applications.