HPPD)-Inhibitor Resistance in Palmer Amaranth (Amaranthus Palmeri S.Wats.)
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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. -
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. -
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. -
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 -
Discovery and Protein Engineering of Baeyer-Villiger Monooxygenases
Discovery and Protein Engineering of Baeyer-Villiger monooxygenases Inauguraldissertation zur Erlangung des akademischen Grades eines Doktors der Naturwissenschaften (Dr. rer. nat.) der Mathematisch-Naturwissenschaftlichen Fakultät der Ernst-Moritz-Arndt-Universität Greifswald vorgelegt von Andy Beier geboren am 11.10.1988 in Parchim Greifswald, den 02.08.2017 I Dekan: Prof. Dr. Werner Weitschies 1. Gutachter: Prof. Dr. Uwe T. Bornscheuer 2. Gutachter: Prof. Dr. Marko Mihovilovic Tag der Promotion: 24.10.2017 II We need to learn to want what we have, not to have what we want, in order to get stable and steady happiness. - The Dalai Lama - III List of abbreviations % Percent MPS Methyl phenyl sulfide % (v/v) % volume per volume MPSO Methyl phenyl sulfoxide % (w/v) % weight per volume MPSO2 Methyl phenyl sulfone °C Degrees Celsius MTS Methyl p-tolyl sulfide µM µmol/L MTSO Methyl p-tolyl sulfoxide aa Amino acids MTSO2 Methyl p-tolyl sulfone + AGE Agarose gel electrophoresis NAD Nicotinamide adenine dinucleotide, oxidized aq. dest. Distilled water NADH Nicotinamide adenine dinucleotide, reduced + BLAST Basic Local Alignment Search NADP Nicotinamide adenine dinucleotide Tool phosphate, oxidized bp Base pair(s) NADPH Nicotinamide adenine dinucleotide phosphate, reduced BVMO Baeyer-Villiger monooxyge- OD600 Optical density at 600 nm nase CHMO Cyclohexanone monooxyge- PAGE Polyacrylamide gel electrophoresis nase Da Dalton PAMO Phenylacetone monooxygenase DMF Dimethyl formamide PCR Polymerase chain reaction DMSO Dimethyl sulfoxide PDB Protein Data Bank DMSO2 Dimethyl sulfone rpm Revolutions per minute DNA Desoxyribonucleic acid rv Reverse dNTP Desoxynucleoside triphosphate SDS Sodium dodecyl sulfate E. coli Escherichia coli SOC Super Optimal broth with Catabolite repression ee Enantiomeric excess TAE TRIS-Acetate-EDTA FAD Flavin adenine dinucleotide TB Terrific broth Fig. -
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. -
Reregistration Eligibility Decision (RED) for Glyphosate
GLYPHOSATE RED September 1993 GLYPHOSATE REREGISTRATION ELIGIBILITY TEAM Office of Pesticide Programs: Special Review and Reregistration Division Eric Feris .................................................. Reregistration Branch Health Effects Division Jane Smith ........................................ Chemical Coordination Branch Krystyna Locke .............................................. Toxicology Branch I Jeff Evans ........................... Occupational and Residential Exposure Branch Randolph Perfetti ......................... Chemistry Branch - Reregistration Support Biological and Economic Analysis Division James G. Saulmon .....................................Biological Analysis Branch Eric Maurer ........................................... Economic Analysis Branch Environmental Fate and Effects Division Candace Brassard ..................................... Ecological Effects Branch Kevin Poff ............................. Environmental Fate and Groundwater Branch Bernice Slutsky ............................ Science Analysis and Coordination Staff Registration Division Mark Perry .......................................... Registration Support Branch Karen P. Hicks ....................................... Fungicide-Herbicide Branch Policy and Special Projects Staff Jean Frane ............................. Food Safety & Regulation Tracking Section Office of General Counsel: Pesticides and Toxic Substances Division Debra Burton ................................................. Pesticides Branch Office of Compliance Monitoring: -
Toxicological Profile for Glyphosate Were
A f Toxicological Profile for Glyphosate August 2020 GLYPHOSATE II DISCLAIMER Use of trade names is for identification only and does not imply endorsement by the Agency for Toxic Substances and Disease Registry, the Public Health Service, or the U.S. Department of Health and Human Services. GLYPHOSATE III FOREWORD This toxicological profile is prepared in accordance with guidelines developed by the Agency for Toxic Substances and Disease Registry (ATSDR) and the Environmental Protection Agency (EPA). The original guidelines were published in the Federal Register on April 17, 1987. Each profile will be revised and republished as necessary. The ATSDR toxicological profile succinctly characterizes the toxicologic and adverse health effects information for these toxic substances described therein. Each peer-reviewed profile identifies and reviews the key literature that describes a substance's toxicologic properties. Other pertinent literature is also presented, but is described in less detail than the key studies. The profile is not intended to be an exhaustive document; however, more comprehensive sources of specialty information are referenced. The focus of the profiles is on health and toxicologic information; therefore, each toxicological profile begins with a relevance to public health discussion which would allow a public health professional to make a real-time determination of whether the presence of a particular substance in the environment poses a potential threat to human health. The adequacy of information to determine a substance's -
New Herbicides for Weeds in Seedling Alfalfa
NEW HERBICIDES FOR WEEDS IN SEEDLING ALFALFA 1 Harold M. Kempen and Joe Voth Abstract: Research suggests that "better mousetraps" for control of seedling weeds in seedling alfalfa are awaiting EPA & CDFA registrations. .Buctril in combination with Poast has been effective in Kern County tests. Until registered, Butyrac in combination with Poast, seems a good option: Pursuit appears to offer the best program because it controls chickweed along with most winter weeds and may suppress yellow nutsedge and johnsongrass. Keywords: Seedling alfalfa, herbicides, grass weeds, broadleaf weeds. INTRODUCTION Poast was recently registered for use in alfalfa. Perhaps that is an omen that something else ~/il1 be registered in the near future as well. It is still possibl~! When I accepted this speaking engagement, I had high hopes that Buctril would be registered by this summer. But that date has passed and the prognosis for labelling of it by next spring is poor. Yes, it is registered in the United States of America, but it isn't registered in sovereign California. This report will focus on three promising treatments: 1. Buctril ME-4 + Poast, Fusilade 2000 or Select; 2. Butyrac Amine + Poast, Fusilade or Select; 3. Pursuit. HERBICIDES MENTIONED IN THIS REPORT Buctril bromoxynil Brominal bromoxynil Butyrac 2,4-DB Butoxone 2,4-DB Poast sethoxydim Fusilade 2000 fluazifop-P-butyl Assure quizalofop Select clethodim Whip fenoxyprop-ethyl Verdict haloxyfop Pursuit imazethapyr Gramoxone Super paraquat BUCTRIL + SELECTIVE GRASS HERBICIDES In Kern County, where we grow almost 90,000 acres and are 4th in alfalfa marketincr in California, we have studied bromoxynil for several years, alone and in combination with the selective grass herbicides: Poast, Fusilade, Assure, Select and Verdict. -
Relating Metatranscriptomic Profiles to the Micropollutant
1 Relating Metatranscriptomic Profiles to the 2 Micropollutant Biotransformation Potential of 3 Complex Microbial Communities 4 5 Supporting Information 6 7 Stefan Achermann,1,2 Cresten B. Mansfeldt,1 Marcel Müller,1,3 David R. Johnson,1 Kathrin 8 Fenner*,1,2,4 9 1Eawag, Swiss Federal Institute of Aquatic Science and Technology, 8600 Dübendorf, 10 Switzerland. 2Institute of Biogeochemistry and Pollutant Dynamics, ETH Zürich, 8092 11 Zürich, Switzerland. 3Institute of Atmospheric and Climate Science, ETH Zürich, 8092 12 Zürich, Switzerland. 4Department of Chemistry, University of Zürich, 8057 Zürich, 13 Switzerland. 14 *Corresponding author (email: [email protected] ) 15 S.A and C.B.M contributed equally to this work. 16 17 18 19 20 21 This supporting information (SI) is organized in 4 sections (S1-S4) with a total of 10 pages and 22 comprises 7 figures (Figure S1-S7) and 4 tables (Table S1-S4). 23 24 25 S1 26 S1 Data normalization 27 28 29 30 Figure S1. Relative fractions of gene transcripts originating from eukaryotes and bacteria. 31 32 33 Table S1. Relative standard deviation (RSD) for commonly used reference genes across all 34 samples (n=12). EC number mean fraction bacteria (%) RSD (%) RSD bacteria (%) RSD eukaryotes (%) 2.7.7.6 (RNAP) 80 16 6 nda 5.99.1.2 (DNA topoisomerase) 90 11 9 nda 5.99.1.3 (DNA gyrase) 92 16 10 nda 1.2.1.12 (GAPDH) 37 39 6 32 35 and indicates not determined. 36 37 38 39 S2 40 S2 Nitrile hydration 41 42 43 44 Figure S2: Pearson correlation coefficients r for rate constants of bromoxynil and acetamiprid with 45 gene transcripts of ECs describing nucleophilic reactions of water with nitriles. -
Corn Herbicides to Control Glyphsoate-Resistant Canola Volunteers
AGRONOMY SCIENCES RESEARCHRESEARCH UPDAUPDATETE Corn Herbicides to Control Glyphosate-Resistant Canola Volunteers 2013 Background Table 1. Herbicide treatments. • With the rapid adoption of glyphosate-resistant corn in Western Treatment Application Rate/Acre Canada, glyphosate-resistant canola volunteers have become a major weed concern to corn producers in the region. 1 Gly Only (Check) 1 L/acre (360g ae) • The Pest Management Regulatory Agency now allows 2 Gly + Dicamba 1 L/acre + 0.243 L/acre herbicides to be tank-mixed if they have individual registrations 3 Gly + 2,4-D 1 L/acre + 0.4 L/acre (600g/L) on the crop and have a common application timing. 4 Gly + MCPA Amine 1 L/acre + 0.45L/acre • Several herbicide options are available to control glyphosate 5 Gly + Bromoxynil 1 L/acre + 0.48 L/acre tolerant canola volunteers in corn; however, some herbicides may have undesirable effects on corn. Gly / Bromoxynil 6 1 L/acre + 0.48 L/acre (Split Application*) Objectives * Glyphosate and bromoxynil applied separately at V3 stage. • Assess crop injury and yield effects of various herbicides tank- mixed with glyphosate to control glyphosate-resistant canola • Herbicide injury scores were recorded at: volunteers in glyphosate-resistant corn. • 3-5 days after treatment • 7-10 days after treatment • Identify the most suitable post-emergence strategy for • 21-24 days after treatment managing glyphosate-resistant canola volunteers in glyphosate-resistant corn. • Other recorded observations include: • Brittle snap counts Study Description • Yield (bu/acre) & moisture (%) • Test weight (lbs/bu) • The study compared the crop response of four industry leading hybrids (Pioneer® brand and competitive) with five different Results herbicide treatments (Table 1).