Paraquat and Diquat

Total Page:16

File Type:pdf, Size:1020Kb

Paraquat and Diquat This report contains the collective views of an international group of experts and does not necessarily represent the decisions or the stated policy of the United Nations Environment Pro- gramme, the International Labour Organisa- tion. or the World Health Organization Environmental Health Criteria 39 PARAQUAT AND DIQUAT Published under the joint sponsorship of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization World Health Organization Geneva, 1984 The Internatfonal Programme on Chemical Safety (IPCS) is a joint venture of the United Nations Environment Programme, the Interna- tional Labour Organisation, and the World Health Organization. The main objective of the IPCS is to carry out and disseminate evaluations of the effects of chemicals on human health and the quality of the environment. Supporting activities include the development of epidemiological, experi- mental laboratory, and risk-assessment methods that could produce inter- nationally comparable results, and the development of manpower in the field of toxicology. Other activities carried out by IPCS include the devel- opment of know-how for coping with chemical accidents, coordination of laboratory testing and epidemiological studies, and promotion of research on the mechanisms of the biological action of chemicals. ISBN 92 4 154099 4 World Health Organization 1984 Publications of the World Health Organization enjoy copyright protec- tion in accordance with the provisions of Protocol 2 of the Universal Copy- right Convention. For rights of reproduction or translation of WHO publica- tions, in part or in tote, application should be made to the Office of Publica- tions, World Health Organization, Geneva, Switzerland. The World Health Organization welcomes such applications. The designations employed and the presentation of the material in this publication do not imply the expression of any opinion whatsoever on the part of the Secretariat of the World Health Organization concerning the legal status of any country, territory, city or area or of its authorities, or con- cerning the delimitation of its frontiers or boundaries The mention of specific companies or of certain manufacturers' products does not imply that they are endorsed or recommended by the World Health Organization in preference to others of a similar nature that are not men- tioned. Errors and omissions excepted, the names of proprietary products are distinguished by initial capital letters. PRINTED IN FINLAND 845229 - VAMMALA - 5500 -3- CONTENT S Page ENVIRONMENTAL HEALTH CRITERIA FOR PARAQUAT AND DIQUAT PARAQUAT 1. SUMMARY AND RECOMMENDATIONS .............13 1.1 Summary ..................... 13 1.1.1 General properties ............ 13 1.1.2 Environmental distribution and tansformat ion - environmental effects . 13 1.1.3 Kinetics and metabolism ......... 14 1.1.4 Effects on experimental animals ..... 14 1.1.5 Effects on man .............. 15 1.2 Recommendations ................. 16 1.2.1 General ................. 16 1.2.2 Prevention and treatment ......... 16 1.2.3 Experimental york ............ 16 IDENTITY, PROPERTIES AND ANALYTICAL METHODS .....18 2.1 Identity .................... 18 2.2 Physical and chemical properties ........ 18 2.3 Analytical methods ............... 19 3. SOURCES IN THE ENVIRONMENT .............. 24 3.1 introduction .................. 24 3.1.1 Industrial technology .......... 24 3.1.2 Impurities ................ 24 3.2 Production and use ............... 25 3.3 Mechanism of the herbicidal effect ....... 28 4. ENVIRONMENTAL DISTRIBUTION AND TRANSPORTATION . 29 4.1 Photochemical degradation ............ 29 4.1.1 Photochemical degradation on plant surfaces ................. 29 4.1.2 Photochemical degradation of paraquat on soil and other mineral surfaces ..... 30 4.2 Microbial degradation .............. 3D 4.3 Environmental adsorption and transformation . 31 4.3.1 Soil ................... 31 4.3.2 Water .................. 34 4.3.3 Air ................... 36 -4- Page 4.3.4 Plants • 38 4.3.5 Animals ................. 40 5. BIOLOGICAL ACTiVITY OF RESIDUES ........... 42 5.1 Soil organisms ................. 42 5.2 Effect of residues on crop yields ........ 42 5.3 Effects on fish and aquatic organisms ...... 43 5.4 Effects on birds ................ 43 6. KINETICS AND METABOLISM ............... 45 6.1 Animal studies ................. 45 6.1.1 Absorption ................ 45 6.1.1.1 Oral absorption ......... 45 6.1.1.2 Pulmonary absorption ...... 45 6.1.1.3 Dermal absorption ........ 46 6.1.2 Distribution ............... 4€ 6.1.3 Metabolic transformation and excretion. 51 6.2 Observations on human beings .......... 52 6.2.1 Observations on paraquat poisoning after ingestion. non-fatal cases ........ 52 6.2.2 Observations on paraqtist poisoning after ingestion: fatal cases .......... 53 6.2.3 Significance of paraquat concentrations in cases of paraquat poisoning ....... 53 6.3 Biochemical mechanisms ............. 54 7. EFFECTS ON ANIMALS .................. 59 7.1 Effects on experimental animals ......... 59 7.1.1 Respiratory system ............ 59 7.1.1.1 Pathomorphological lung studies .59 7.1.1.2 Species differences in lung injury ............. 64 7.1.1.3 Functional lung studies ..... 65 7.1.2 Renal system ............... 6.5 7.1.3 Gastrointestinal tract and liver ..... 65 7.1.4 Skin and eyes .............. 66 7.1.5 Other systems .............. 67 7.1.6 Effects on reproduction, embryotoxicity, and teratogenicity ............ 67 7.1.6.1 Effects on reproduction ..... 67 7.1.6.2 Embryotoxicity and teratiogenicity 68 7.1.7 Mutagenicity ............... 68 7.1.8 Carcinogenicity ............. 69 7.2 Effects on farm animals ............. 69 -5- p ag e 7.3 Dose-effect of paraquat 70 7.4 Methods for decreasing paraquat toxicity . 71 7.5 Relation between age, sex, and toxicity .....72 8. EFFECTS ON MAN ....................74 8.1 Accidental and suicidal poisoning ........ 74 8.1.1 Case reports ............... 74 8.1.2 Distribution of cases of paraquat p oisoning ................ 74 8.1.3 Route of entry .............. 76 8.1.4 Formulations ............... 76 8.1.5 Dose ................... 76 8.1.6 Clinical and pathomorphological data relating to fatal paraquat poisoning . 78 8.1.6.1 Respiratory system ....... 78 8.1.6.2 Renal system .......... 79 8.1.6.3 Gastrointestinal system, the Liver, and the pancreas ..... 79 8.1.6.4 Cardiovascular system ...... 80 8.1.6.5 Central nervous system ..... 80 8.1.6.6 Adrenal glands ......... 80 8.1.6.7 Pregnancy ............ 80 8.1.7 Recovery from paraquat poisoning ..... 81 8.2 Occupational exposure .............. 83 8.2.1 Epidemiological studies and case reports 53 8.2.1.1 Spraying personnel ....... 83 8.2.1.2 Formulation workers ....... 86 8.2.2 Cases of occupational poisoning and local caustic effects ............. 87 8.2.2.1 Oral ingestion ......... 87 8.2.2.2 Derinal absorption ........ 88 8.2.2.3 Local skin and nail effects . 89 8.2.2.4 Ocular damage .......... 89 8.2.2.5 Inhalation ........... 90 8.3 Use of marijuana contaminated by paraquat 90 8.4 Guidelines for the treatment of paraquat p oisoning .................... 91 9. EvALUATION OF RISKS FOR HUMAN HEALTH AND EFFECTS ON THE ENVIRONMENT ...................93 9.1 Exposure ....................93 9.2 Poisoning by paraquat ..............95 9.2,1 Suicidal ingestion ............95 9.2.2 Accidental poisoning ...........95 9.2.3 Occupational poisoning ..........95 -6- Page 9.3 Occupational exposure 96 9.4 Effects 96 9.4.1 Paraquat toxicity in animals .......96 9.4.2 Paraquat determination in biological fluids and tissues ............97 9.5 Earlier evaluations by international bodies 97 9.6 Conclusions ...................97 REFERENCES........................99 M. Page DIQUAT )-. SUMMARY AND RECOMMENDATIONS . 131 1.1 Summary ..................... 131 1.1.1 General properties ............ 131 1.1.2 Environmental distribution and transformation - environmental effects 131 1.1.3 Kinetics and metabolism ......... 132 1.1.4 Effects on animals ............ 132 1.1.5 Effects on man .............. 133 1.2 Recommendations ................. 133 1.2.1 General ................. 133 1.2.2 Prevention and treatment ......... 133 1.2.3 Experimental work ............ 134 PROPERTIES AND ANALYTICAL METHODS .......... 135 2.1 Physical and chemical properties ........ 135 2.2 Analytical procedures ..............136 SOURCES IN THE ENVIRONMENT ..............138 3.1 Production and uses ............... 138 ENVIRONMENTAL DISTRIBUTION, LEVELS, AND EXPOSURE . 139 4.1 Photochemical and microbial degradation of diquat .................... 139 4.1.1 Photochemical degradation ........ 139 4.1.2 Microbial degradation .......... 140 4.2 Diquat adsorption, residue levels, and exposure in soil ................ 140 4.2.1 Diquat adsorption on soil particles . 140 4.2.2 Residue levels of diquat in soils . 141 4.2.3 Effect of resi6sa1 diquat on soil biological activity, and on plants and crop yields ............... 141 4.3 Diquat transformation, residue levels, and effects on aquatic organisms and crops ..... 142 4.3,1 Transformation and residue levels of diquat in water ............. 142 4.3.2 Effects of residual diquat on aquatic organisms and crops ........... 143 4.4 Diquat exposure and residue levels in plants and animals ................... 144 4.4.1 Plants .................. 144 4.4.2 Animals ................. 145 -8- 4.5 Diquat levels in air and exposure of workers . 146 5. KINETICS AND METABOLISM ............... 146 5.1 Animal studies ................. 148 .1.1 Absorption ...............
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.
    [Show full text]
  • 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
    [Show full text]
  • 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.
    [Show full text]
  • Environmental Health Criteria 39 PARAQUAT and DIQUAT
    Environmental Health Criteria 39 PARAQUAT AND DIQUAT Please note that the layout and pagination of this web version are not identical with the printed version. Paraquat and diquat (EHC 39, 1984) INTERNATIONAL PROGRAMME ON CHEMICAL SAFETY ENVIRONMENTAL HEALTH CRITERIA 39 PARAQUAT AND DIQUAT This report contains the collective views of an international group of experts and does not necessarily represent the decisions or the stated policy of the United Nations Environment Programme, the International Labour Organisation, or the World Health Organization. Published under the joint sponsorship of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization World Health Orgnization Geneva, 1984 The International Programme on Chemical Safety (IPCS) is a joint venture of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization. The main objective of the IPCS is to carry out and disseminate evaluations of the effects of chemicals on human health and the quality of the environment. Supporting activities include the development of epidemiological, experimental laboratory, and risk-assessment methods that could produce internationally comparable results, and the development of manpower in the field of toxicology. Other activities carried out by the IPCS include the development of know-how for coping with chemical accidents, coordination of laboratory testing and epidemiological studies, and promotion of research on the mechanisms of the biological action of chemicals. ISBN 92 4 154099 4 The World Health Organization welcomes requests for permission to reproduce or translate its publications, in part or in full. Applications and enquiries should be addressed to the Office of Publications, World Health Organization, Geneva, Switzerland, which will be glad to provide the latest information on any changes made to the text, plans for new editions, and reprints and translations already available.
    [Show full text]
  • Diquat Ecological Risk Assessment, Final Report
    Utah State University DigitalCommons@USU All U.S. Government Documents (Utah Regional U.S. Government Documents (Utah Regional Depository) Depository) 11-2005 Diquat Ecological Risk Assessment, Final Report Bureau of Land Management Follow this and additional works at: https://digitalcommons.usu.edu/govdocs Part of the Life Sciences Commons, and the Physical Sciences and Mathematics Commons Recommended Citation Bureau of Land Management, "Diquat Ecological Risk Assessment, Final Report" (2005). All U.S. Government Documents (Utah Regional Depository). Paper 107. https://digitalcommons.usu.edu/govdocs/107 This Report is brought to you for free and open access by the U.S. Government Documents (Utah Regional Depository) at DigitalCommons@USU. It has been accepted for inclusion in All U.S. Government Documents (Utah Regional Depository) by an authorized administrator of DigitalCommons@USU. For more information, please contact [email protected]. Bureau of Land Management Reno, Nevada Diquat Ecological Risk Assessment Final Report November 2005 Bureau of Land Management Contract No. NAD010156 ENSR Document Number 09090-020-650 Executive Summary The United States Department of the Interior (USDI) Bureau of Land Management (BLM) is proposing a program to treat vegetation on up to six million acres of public lands annually in 17 western states in the continental United States (US) and Alaska. As part of this program, the BLM is proposing the use of ten herbicide active ingredients (a.i.) to control invasive plants and noxious weeds on approximately one million of the 6 million acres proposed for treatment. The BLM and its contractor, ENSR, are preparing a Vegetation Treatments Programmatic Environmental Impact Statement (EIS) to evaluate this and other proposed vegetation treatment methods and alternatives on lands managed by the BLM in the western continental US and Alaska.
    [Show full text]
  • 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®,
    [Show full text]
  • Classification of Herbicides
    Title of the course : Weed Management Credit: 3(2+1) Class : 3rd Year IInd Semester Title of the topic : Principles of weed management College : Krishi vigyan Kendra,College of Agriculture, Rewa, JNKVV, Jabalpur Name of Teacher : Dr. (Mrs.) Smita Singh Classification of Herbicides Herbicides: Chemical method of weed control is very effective in certain cases and have great scope provided the herbicides are cheap, efficient and easily available. The chemicals used for killing the weeds or inhibiting growth of weeds are called herbicides (Weedicides). Classification of Herbicides: Herbicides are classified in different ways: A) First Group Chemical Herbicides: I) Classification of herbicides according to chemical composition. II) Classification of herbicides according to their use. III) Classification of herbicides based on time of application. IV) Classification of herbicides according to Formulation. V) Classification of herbicides according to residual effect. B) Second Group – Bio herbicides C) Third Group herbicidal mixtures. Classification of herbicide I) Classification of Herbicide Based on Chemical Nature or Composition Compounds having chemical affinities are grouped together. This is useful in liting and characterising herbicides. i) Inorganic Herbicides:Contain no carbon actions in their molecules. These were the first chemicals used for weed control before the introduction of the organic compounds, example are: a) Acids:Arsenic acid, arsenious acid, arsenic trioxide sulphuric acid. b) Salts:Borax, copper sulphate, ammonium sulphate, Na chlorate , Na arsenite , copper nitrate. ii) Organic Herbicides:Oils and non oils contain carbon and hydrogen in their molecules. a) Oils: Diesel oil, standard solvent, xylene-type, aromatic oils, polycyclic , aromatic oils etc. b) Aliphatics:Dalapon, TCA, Acrolein, Glyphosphate methyl bromide.
    [Show full text]
  • Effects of Paraquat and Alachlor on Soil Microorganisms in Peat Soil
    Pertanika 15(2),121-125 (1992) Effects of Paraquat and Alachlor on Soil Microorganisms in Peat Soil ISMAIL SAHID, AINON HAMZAH and PARIDAH M. ARIS Faculty of Life Sciences Universiti Kebangsaan Malaysia 43600 Bangi, Selangor, Malaysia Keywords: AlacWor, paraquat, microbes, peat soil. ABSTRAK Satu kajian telah dijalankan untuk melihat kesan alachlor dan paraquat ke atas aktiviti mikrob dalam tanah gambut. Kesan racun rumpai ke atas pembebasan CO2 dan aktiviti phosphatase dimonitor selama 12 minggu. Hasil yang diperolehi menunjukkan paraquat dan alachlor yang disembur kepada tanah menyebabkan peningkatan pembebasan CO di peringkat awal pengeraman tetapi berkurangan selepas 53 han. Lebih banyak CO dibebaskan 2 2 dari tanah yang dirawat dengan alachlor berbanding dengan tanah yang dirawat dengan paraquat. Aktiviti phosphatase meningkat di peringkat awal pengeraman bagi tanah yang diperlakukan dengan sama ada alachlor atau paraquat. Aktiviti phosphatase meningkat di peringkat awal pengeraman bagi tanah yang diperlakukan dengan sama ada alachlor atau paraquat tetapi aktiviti phosphatase berkurangan seiepas 12 han eraman. Populasi kulat dan bakteria dipengaruhi oleh kedua-dua racun rumpai yang diuji. Pada kepekatan 250 ppm, alachlor dan paraquat, masing-masing menyebabkan pengurangan populasi bakteria kira-kira 78 dan 95%. Alachlor didapati lebih toksik terhadap kulat berbanding paraquat. ABSTRACT A study was carried out to investigate the effects ofalachlor and paraquat on microbial activities in peat soil. Effects ofthe herbicides on CO2 evolution and phosphatase activity were monitored for 12 weeks in ambient conditions. The results showed that paraquat and alachlor caused an initial increase in CO2 released and subsequently decreased after 53 days of incubation. Comparatively, more CO2 was released from the soil treated with alachlor than that treated with paraquat.
    [Show full text]
  • Chemical Weed Control
    2014 North Carolina Agricultural Chemicals Manual The 2014 North Carolina Agricultural Chemicals Manual is published by the North Carolina Cooperative Extension Service, College of Agriculture and Life Sciences, N.C. State University, Raleigh, N.C. These recommendations apply only to North Carolina. They may not be appropriate for conditions in other states and may not comply with laws and regulations outside North Carolina. These recommendations are current as of November 2013. Individuals who use agricultural chemicals are responsible for ensuring that the intended use complies with current regulations and conforms to the product label. Be sure to obtain current information about usage regulations and examine a current product label before applying any chemical. For assistance, contact your county Cooperative Extension agent. The use of brand names and any mention or listing of commercial products or services in this document does not imply endorsement by the North Carolina Cooperative Extension Service nor discrimination against similar products or services not mentioned. VII — CHEMICAL WEED CONTROL 2014 North Carolina Agricultural Chemicals Manual VII — CHEMICAL WEED CONTROL Chemical Weed Control in Field Corn ...................................................................................................... 224 Weed Response to Preemergence Herbicides — Corn ........................................................................... 231 Weed Response to Postemergence Herbicides — Corn ........................................................................
    [Show full text]
  • Pesticides EPA-738-F-96-018 Environmental Protection and Toxic Substances August 1997 Agency (7508W) R.E.D
    United States Prevention, Pesticides EPA-738-F-96-018 Environmental Protection And Toxic Substances August 1997 Agency (7508W) R.E.D. FACTS Paraquat Dichloride Pesticide All pesticides sold or distributed in the United States must be Reregistration registered by EPA, based on scientific studies showing that they can be used without posing unreasonable risks to people or the environment. Because of advances in scientific knowledge, the law requires that pesticides which were first registered before November 1, 1984, be reregistered to ensure that they meet today's more stringent standards. Under the Food Quality Protection Act of 1996, EPA must consider the increased susceptibility of infants and children to pesticide residues in food, as well as aggregate exposure of the public to pesticide residues from all sources, and the cumulative effects of pesticides and other compounds with a common mechanism of toxicity in establishing and reassessing tolerances. In evaluating pesticides for reregistration, EPA obtains and reviews a complete set of studies from pesticide producers, describing the human health and environmental effects of each pesticide. The Agency develops any mitigation measures or regulatory controls needed to effectively reduce each pesticide's risks. EPA then reregisters pesticides that can be used without posing unreasonable risks to human health or the environment. When a pesticide is eligible for reregistration, EPA explains the basis for its decision in a Reregistration Eligibility Decision (RED) document. This fact sheet summarizes the information in the RED document for reregistration case 0262, paraquat dichloride (commonly referred to as paraquat). Use Profile Paraquat dichloride is a herbicide currently registered to control weeds and grasses in many agricultural and non-agricultural areas.
    [Show full text]
  • Combinations of Penoxsulam and Diquat As Foliar Applications for Control of Waterhyacinth and Common Salvinia: Evidence of Herbicide Antagonism
    J. Aquat. Plant Manage. 48: 21-25 Combinations of Penoxsulam and Diquat as Foliar Applications for Control of Waterhyacinth and Common Salvinia: Evidence of Herbicide Antagonism RYAN M. WERSAL1 AND J. D. MADSEN1,2 ABSTRACT INTRODUCTION Waterhyacinth (Eichhornia crassipes [Mart.] Solms) and Waterhyacinth (Eichhornia crassipes [Mart.] Solms) and common salvinia (Salvinia minima Baker) are two floating common salvinia (Salvinia minima Baker) are widespread aquatic plants that can cause wide-spread problems in the problems in waterways throughout the southern United southern United States. These species can cause reductions States. Waterhyacinth is an invasive free-floating aquatic in ecosystem function as well as the abundance of native plant from the tropical and subtropical regions of South plant species. Herbicides are often used in an attempt to America (Holm et al. 1991). Waterhyacinth effectively dou- control both species; however, few recommendations exist bles the number of plants within 12.5 d (Penfound and Ear- for common salvinia. Penoxsulam (2-(2,2-difluoroethoxy)-N- le 1948), increases dry biomass at a rate of 1.2% d-1, and (5,8 dimethoxy [1,2,4] triazolo [1,5-c] pyrimidin-2-yl)-6 (trif- peak biomass can reach a maximum of 2.5 kg m-2 under op- luoromethyl) benzenesulfonamide) is newly registered for timal conditions (Center and Spencer 1981). Waterhya- use in aquatic environments and is efficacious on floating cinth impedes the recreational use of rivers and lakes plants as a submersed application; however, foliar applica- (fishing, swimming, and boat traffic) and the generation of tion rates are largely undefined. The objectives of these stud- hydroelectric power.
    [Show full text]
  • HPPD) Inhibitor Herbicide Resistance in Waterhemp (Amaranthus Tuberculatus
    University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln U.S. Department of Agriculture: Agricultural Publications from USDA-ARS / UNL Faculty Research Service, Lincoln, Nebraska 5-6-2019 Using RNA-seq to characterize responses to 4 hydroxyphenylpyruvate dioxygenase (HPPD) inhibitor herbicide resistance in waterhemp (Amaranthus tuberculatus) Daniel R. Kohlhase Iowa State University Jamie A. O’Rourke (USDA)–Agricultural Research Service Micheal D. K. Owen Iowa State University, [email protected] Michelle A. Graham (USDA)–Agricultural Research Service, [email protected] Follow this and additional works at: https://digitalcommons.unl.edu/usdaarsfacpub Kohlhase, Daniel R.; O’Rourke, Jamie A.; Owen, Micheal D. K.; and Graham, Michelle A., "Using RNA-seq to characterize responses to 4 hydroxyphenylpyruvate dioxygenase (HPPD) inhibitor herbicide resistance in waterhemp (Amaranthus tuberculatus)" (2019). Publications from USDA-ARS / UNL Faculty. 2163. https://digitalcommons.unl.edu/usdaarsfacpub/2163 This Article is brought to you for free and open access by the U.S. Department of Agriculture: Agricultural Research Service, Lincoln, Nebraska at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Publications from USDA-ARS / UNL Faculty by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Kohlhase et al. BMC Plant Biology (2019) 19:182 https://doi.org/10.1186/s12870-019-1795-x RESEARCH ARTICLE Open Access Using RNA-seq to characterize responses to 4-hydroxyphenylpyruvate dioxygenase (HPPD) inhibitor herbicide resistance in waterhemp (Amaranthus tuberculatus) Daniel R. Kohlhase1, Jamie A. O’Rourke2, Micheal D. K. Owen1* and Michelle A. Graham2* Abstract Background: Waterhemp (Amaranthus tuberculatus (Moq.) J.D. Sauer) is a problem weed commonly found in the Midwestern United States that can cause crippling yield losses for both maize (Zea mays L.) and soybean (Glycine max L.
    [Show full text]