Mechanism of Resistance to Mesotrione in an Amaranthus Tuberculatus Population from Nebraska, USA
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
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. -
Toxicidade De Herbicidas Pós- Emergentes Em Cultivares De Feijão-Caupi
TOXICIDADE DE HERBICIDAS PÓS- EMERGENTES EM CULTIVARES DE FEIJÃO-CAUPI THIAGO REIS PRADO 2016 THIAGO REIS PRADO TOXICIDADE DE HERBICIDAS PÓS-EMERGENTES EM CULTIVARES DE FEIJÃO-CAUPI Dissertação apresentada à Universidade Estadual do Sudoeste da Bahia, Campus de Vitória da Conquista, para obtenção do título de Mestre em Agronomia. Orientador: Prof. D.Sc.Alcebíades Rebouças São José VITÓRIA DA CONQUISTA BAHIA - BRASIL 2016 P915t Prado, Thiago Reis. Toxicidade de herbicidas pós-emergentes em cultivares de feijão-caupi. / Thiago Reis Prado. 55f. Orientador (a): D.Sc. Alcebíades Rebouças São José. Dissertação (mestrado) – Universidade Estadual do Sudoeste da Bahia, Programa de Pós-graduação em Agronomia, área de concentração em Fitotecnia. Vitória da Conquista, 2016. Referências: f. 50-55. 1. Vigna unguiculata - Cultivo. 2. Controle químico. 3. Planta daninha. 4. Fitotoxidade. I. São José, Alcebíades Rebouças II. Universidade Estadual do Sudoeste da Bahia, Programa de Pós-Graduação em Agronomia, área de Concentração em Fitotecnia. III. T. CDD: 633.33 Catalogação na fonte : Juliana Teixeira de Assunção – CRB 5/18 90 UESB – Campus Vitória da Conquista - BA Aos meus pais, Paulo Soares Prado e Maria José Reis Prado, que, sempre dedicados à minha educação e fortes na fé, atuam de forma singular com seus ensinamentos e suas orações. Dedico Agradecimentos A Deus, por iluminar minha vida e guiar por todos os caminhos. Aos meus pais, Paulo Soares Prado e Maria José Reis Prado, pelo amor e por apoiarem sempre as decisões para realização dos meus sonhos. Ao Prof. Dr. Alcebíades Rebouças São José, pela confiança, orientação, compreensão e amizade durante todo o curso do mestrado. -
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®), -
CFS Science Comments I
April 27, 2012 Docket No. APHIS–2010–0103 Regulatory Analysis and Development PPD, APHIS Station 3A-03.8 4700 River Road Unit 118 Riverdale, MD 20737-1238 Comments to USDA APHIS on Environmental Assessment for the Determination of Nonregulated Status of Herbicide-Tolerant DAS-40278-9 Corn, Zea mays, Event DAS- 40278-9 Center for Food Safety, Science Comments I – By Bill Freese, Science Policy Analyst These comments submitted by Center for Food Safety are one of three sets of comments from our organization. Legal comments and a second set of science comments are also being submitted. The references cited have been uploaded as supporting materials. The filenames for these documents match the citations in the text, and are all incorporated as (e.g. Benbrook 2012). Full citations are included at the end of each section. THE IMPACT OF DAS-40278-9 ON CORN HERBICIDE USE Summary of herbicide use Dow’s DAS-402787-9 corn is genetically engineered for resistance to 2,4-D and quizalofop, and if deregulated would be marketed with additional resistance to glyphosate and likely glufosinate – fostering greater use of three to four herbicide classes. APHIS must assess DAS-42078-9 as Dow intends it to be used, as a weed control system. DAS-40278-9 eliminates the risk of crop injury that currently limits 2,4-D use on corn, and is thus reasonably projected to trigger an up to 30-fold increase in the use of this toxic herbicide on corn, equivalent to a four-fold increase in overall agricultural use of 2,4-D, by the end of the decade. -
State of New York City's Plants 2018
STATE OF NEW YORK CITY’S PLANTS 2018 Daniel Atha & Brian Boom © 2018 The New York Botanical Garden All rights reserved ISBN 978-0-89327-955-4 Center for Conservation Strategy The New York Botanical Garden 2900 Southern Boulevard Bronx, NY 10458 All photos NYBG staff Citation: Atha, D. and B. Boom. 2018. State of New York City’s Plants 2018. Center for Conservation Strategy. The New York Botanical Garden, Bronx, NY. 132 pp. STATE OF NEW YORK CITY’S PLANTS 2018 4 EXECUTIVE SUMMARY 6 INTRODUCTION 10 DOCUMENTING THE CITY’S PLANTS 10 The Flora of New York City 11 Rare Species 14 Focus on Specific Area 16 Botanical Spectacle: Summer Snow 18 CITIZEN SCIENCE 20 THREATS TO THE CITY’S PLANTS 24 NEW YORK STATE PROHIBITED AND REGULATED INVASIVE SPECIES FOUND IN NEW YORK CITY 26 LOOKING AHEAD 27 CONTRIBUTORS AND ACKNOWLEGMENTS 30 LITERATURE CITED 31 APPENDIX Checklist of the Spontaneous Vascular Plants of New York City 32 Ferns and Fern Allies 35 Gymnosperms 36 Nymphaeales and Magnoliids 37 Monocots 67 Dicots 3 EXECUTIVE SUMMARY This report, State of New York City’s Plants 2018, is the first rankings of rare, threatened, endangered, and extinct species of what is envisioned by the Center for Conservation Strategy known from New York City, and based on this compilation of The New York Botanical Garden as annual updates thirteen percent of the City’s flora is imperiled or extinct in New summarizing the status of the spontaneous plant species of the York City. five boroughs of New York City. This year’s report deals with the City’s vascular plants (ferns and fern allies, gymnosperms, We have begun the process of assessing conservation status and flowering plants), but in the future it is planned to phase in at the local level for all species. -
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 -
Amaranthus Palmeri) in 2,4-D , Glufosinate-, and Glyphosate-Resistant Soybean
Weed Technology Management of glyphosate-resistant Palmer – www.cambridge.org/wet amaranth (Amaranthus palmeri) in 2,4-D , glufosinate-, and glyphosate-resistant soybean 1 2 3 4 Research Article Chandrima Shyam , Parminder S. Chahal , Amit J. Jhala and Mithila Jugulam 1 2 Cite this article: Shyam C, Chahal PS, Jhala AJ, Graduate Student, Department of Agronomy, Kansas State University, Manhattan, KS, USA; Postdoctoral Research 3 Jugulam M (2021) Management of glyphosate- Associate, Department of Agronomy and Horticulture, University of Nebraska-Lincoln, Lincoln, NE, USA; Associate resistant Palmer amaranth (Amaranthus Professor, Department of Agronomy and Horticulture, University of Nebraska-Lincoln, Lincoln, NE, USA and palmeri) in 2,4-D–, glufosinate-, and 4Professor, Department of Agronomy, Kansas State University, Manhattan, KS, USA glyphosate-resistant soybean. Weed Technol. 35:136–143. doi: 10.1017/wet.2020.91 Abstract Received: 7 May 2020 Glyphosate-resistant (GR) Palmer amaranth is a problematic, annual broadleaf weed in Revised: 7 July 2020 soybean production fields in Nebraska and many other states in the United States. Soybean Accepted: 29 July 2020 TM First published online: 18 August 2020 resistant to 2,4-D, glyphosate, and glufosinate (Enlist E3 ) has been developed and was first grown commercially in 2019. The objectives of this research were to evaluate the effect of herbicide Associate Editor: programs applied PRE, PRE followed by (fb) late-POST (LPOST), and early-POST (EPOST) fb Kevin Bradley, University of Missouri LPOST on GR Palmer amaranth control, density, and biomass reduction, soybean injury, and ’ Nomenclature: yield. Field experiments were conducted near Carleton, NE, in 2018, and 2019 in a grower sfield 2,4-D chlorimuron-ethyl; cloransulam-methyl; infested with GR Palmer amaranth in 2,4-D–, glyphosate-, and glufosinate-resistant soybean. -
Delayed Fluorescence Imaging of Photosynthesis Inhibitor and Heavy Metal Induced Stress in Potato
Cent. Eur. J. Biol. • 7(3) • 2012 • 531-541 DOI: 10.2478/s11535-012-0038-z Central European Journal of Biology Delayed fluorescence imaging of photosynthesis inhibitor and heavy metal induced stress in potato Research Article Jaka Razinger1,*, Luka Drinovec2, Maja Berden-Zrimec3 1Agricultural Institute of Slovenia, 1000 Ljubljana, Slovenia 2Aerosol d.o.o., 1000 Ljubljana, Slovenia 3Institute of Physical Biology, 1000 Ljubljana, Slovenia Received 09 November 2011; Accepted 13 March 2012 Abstract: Early chemical-induced stress in Solanum tuberosum leaves was visualized using delayed fluorescence (DF) imaging. The ability to detect spatially heterogeneous responses of plant leaves exposed to several toxicants using delayed fluorescence was compared to prompt fluorescence (PF) imaging and the standard maximum fluorescence yield of PSII measurements (Fv/Fm). The toxicants used in the study were two photosynthesis inhibitors (herbicides), 100 μM methyl viologen (MV) and 140 μM diuron (DCMU), and two heavy metals, 100 μM cadmium and 100 μM copper. The exposure times were 5 and 72 h. Significant photosynthesis-inhibitor effects were already visualized after 5 h. In addition, a significant reduction in the DF/PF index was measured in DCMU- and MV-treated leaves after 5 h. In contrast, only DCMU-treated leaves exhibited a significant decrease in Fv/Fm after 5 h. All treatments resulted in a significant decrease in the DF/PF parameter after 72 h of exposure, when only MV and Cd treatment resulted in visible symptoms. Our study highlights the power of delayed fluorescence imaging. Abundant quantifiable spatial information was obtained with the instrumental setup. Delayed fluorescence imaging has been confirmed as a very responsive and useful technique for detecting stress induced by photosynthesis inhibitors or heavy metals. -
Effects of Chronic Exposure to the Herbicide, Mesotrione, on Spiders
Susquehanna University Scholarly Commons Senior Scholars Day Apr 28th, 12:00 AM - 12:00 AM Effects of Chronic Exposure to the Herbicide, Mesotrione, on Spiders Maya Khanna Susquehanna University Joseph Evans Susquehanna University Matthew Persons Susquehanna University Follow this and additional works at: https://scholarlycommons.susqu.edu/ssd Khanna, Maya; Evans, Joseph; and Persons, Matthew, "Effects of Chronic Exposure to the Herbicide, Mesotrione, on Spiders" (2020). Senior Scholars Day. 34. https://scholarlycommons.susqu.edu/ssd/2020/posters/34 This Event is brought to you for free and open access by Scholarly Commons. It has been accepted for inclusion in Senior Scholars Day by an authorized administrator of Scholarly Commons. For more information, please contact [email protected]. Effects of Chronic Exposure to the Herbicide, Mesotrione on Spiders Maya Khanna, Joseph Evans, and Matthew Persons Department of Biology, Susquehanna University, PA 17870 Tigrosa helluo Trochosa ruricola Mecaphesa asperata Frontinella pyramitela Tetragnatha laboriosa Hogna lenta Pisaurina mira Abstract Methods All spiders were collected on Table 1. The predicted lethality of mesotrione on each spider species based upon soil association levels and species size. Toxicity is predicted to increase with smaller size and Mesotrione is a widely used agricultural herbicide and is frequently used alone or as an adjuvant for the Susquehanna University’s campus. Each spider was housed in a 473 ml (16oz) greater soil contact. Sample sizes for each species are indicated to the left. A total of 615 herbicides glyphosate and atrazine. The effects of mesotrione are largely untested on beneficial non-target spiders were used in this study. species such as spiders. -
(Aminomethyl)Phosphonic Acid, and Glyphosate-Based Formulations for Genotoxicity and Oxidative Stress Using in Vitro Approaches
Evaluation of Glyphosate, (Aminomethyl)phosphonic Acid, and Glyphosate-Based Formulations for Genotoxicity and Oxidative Stress Using In Vitro Approaches Stephanie L. Smith-Roe, Ph.D. Genetic Toxicology Group Biomolecular Screening Branch National Toxicology Program National Institute of Environmental Health Sciences EMGS 50th Annual Meeting September 23, 2019 Disclaimer The findings and conclusions in this presentation are those of the presenter and do not necessarily reflect the views, policies, or conclusions of NTP or any other U.S. Federal agency. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. NTP studies of glyphosate Toxicity Report No. 16: 13-week study with glyphosate in feed (1992) • Nominated by California Regional Water Quality Control Board North Coast Region (1981) – Glyphosate being found in water runoff in areas of use • NTP selected glyphosate for toxicity evaluation because of: – Expanding use – Potential for human exposure – The lack of published reports concerning comprehensive toxicity or carcinogenicity evaluations NTP studies of glyphosate Toxicity Report No. 16: 13-week study with glyphosate in feed (1992) Top dose for rats ∼3,400 mg/kg/day (males & females) Top dose for mice ∼10,800 and ~12,000 mg/kg/day (males & females, respectively) • No gross lesions at necropsy (rats or mice) • Micronucleus assay was negative in male and female mice (also 13-week exposure via feed) • Bacterial mutagenicity tests were negative • ADME studies indicated low absorption -
CAS Number Index
2334 CAS Number Index CAS # Page Name CAS # Page Name CAS # Page Name 50-00-0 905 Formaldehyde 56-81-5 967 Glycerol 61-90-5 1135 Leucine 50-02-2 596 Dexamethasone 56-85-9 963 Glutamine 62-44-2 1640 Phenacetin 50-06-6 1654 Phenobarbital 57-00-1 514 Creatine 62-46-4 1166 α-Lipoic acid 50-11-3 1288 Metharbital 57-22-7 2229 Vincristine 62-53-3 131 Aniline 50-12-4 1245 Mephenytoin 57-24-9 1950 Strychnine 62-73-7 626 Dichlorvos 50-23-7 1017 Hydrocortisone 57-27-2 1428 Morphine 63-05-8 127 Androstenedione 50-24-8 1739 Prednisolone 57-41-0 1672 Phenytoin 63-25-2 335 Carbaryl 50-29-3 569 DDT 57-42-1 1239 Meperidine 63-75-2 142 Arecoline 50-33-9 1666 Phenylbutazone 57-43-2 108 Amobarbital 64-04-0 1648 Phenethylamine 50-34-0 1770 Propantheline bromide 57-44-3 191 Barbital 64-13-1 1308 p-Methoxyamphetamine 50-35-1 2054 Thalidomide 57-47-6 1683 Physostigmine 64-17-5 784 Ethanol 50-36-2 497 Cocaine 57-53-4 1249 Meprobamate 64-18-6 909 Formic acid 50-37-3 1197 Lysergic acid diethylamide 57-55-6 1782 Propylene glycol 64-77-7 2104 Tolbutamide 50-44-2 1253 6-Mercaptopurine 57-66-9 1751 Probenecid 64-86-8 506 Colchicine 50-47-5 589 Desipramine 57-74-9 398 Chlordane 65-23-6 1802 Pyridoxine 50-48-6 103 Amitriptyline 57-92-1 1947 Streptomycin 65-29-2 931 Gallamine 50-49-7 1053 Imipramine 57-94-3 2179 Tubocurarine chloride 65-45-2 1888 Salicylamide 50-52-2 2071 Thioridazine 57-96-5 1966 Sulfinpyrazone 65-49-6 98 p-Aminosalicylic acid 50-53-3 426 Chlorpromazine 58-00-4 138 Apomorphine 66-76-2 632 Dicumarol 50-55-5 1841 Reserpine 58-05-9 1136 Leucovorin 66-79-5 -
Orfadin, INN-Nitisinone
SCIENTIFIC DISCUSSION 1. Introduction 1.1 Problem statement Hereditary tyrosinaemia type 1 (HT-1) is a devastating inherited disease, mainly of childhood. It is characterised by severe liver dysfunction, impaired coagulation, painful neurological crises, renal tubular dysfunction and a considerable risk of hepatocellular carcinoma (Weinberg et al. 1976, Halvorsen 1990, Kvittingen 1991, van Spronsen et al. 1994, Mitchell et al. 1995). The condition is caused by an inborn error in the final step of the tyrosine degradation pathway (Lindblad et al. 1977). The incidence of HT-1 in Europe and North America is about one in 100,000 births, although in certain areas the incidence is considerably higher. In the province of Quebec, Canada, it is about one in 20,000 births (Mitchell et al. 1995). The mode of inheritance is autosomal recessive. The primary enzymatic defect in HT-1 is a reduced activity of fumarylacetoacetate hydrolase (FAH) in the liver, the last enzyme in the tyrosine degradation pathway. As a consequence, fumaylacetoacetate (FAA) and maleylacetoacetate (MAA), upstream of the enzymatic block, accumulate. Both intermediates are highly reactive and unstable and cannot be detected in the serum or urine of affected children. Degradation products of MAA and FAA are succinylacetone (SA) and succinylacetoacetate (SAA) which are (especially SA) toxic, and which are measurable in the serum and urine and are hallmarks of the disease. SA is also an inhibitor of Porphobilinogen synthase (PBG), leading to an accumulation of 5-aminolevulinate (5-ALA) which is thought to be responsible for the neurologic crises resembling the crises of the porphyrias. The accumulation of toxic metabolites starts at birth and the severity of phenotype is reflected in the age of onset of symptoms (Halvorsen 1990, van Spronsen et al.