Redox Imbalance Caused by Pesticides: a Review of OPENTOX-Related Research
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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. -
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®), -
40 CFR Ch. I (7–1–18 Edition) § 455.61
§ 455.61 40 CFR Ch. I (7–1–18 Edition) from: the operation of employee show- § 455.64 Effluent limitations guidelines ers and laundry facilities; the testing representing the degree of effluent of fire protection equipment; the test- reduction attainable by the applica- ing and emergency operation of safety tion of the best available tech- showers and eye washes; or storm nology economically achievable water. (BAT). (d) The provisions of this subpart do Except as provided in 40 CFR 125.30 not apply to wastewater discharges through 125.32, any existing point from the repackaging of microorga- source subject to this subpart must nisms or Group 1 Mixtures, as defined achieve effluent limitations rep- under § 455.10, or non-agricultural pes- resenting the degree of effluent reduc- ticide products. tion attainable by the application of the best available technology economi- § 455.61 Special definitions. cally achievable: There shall be no dis- Process wastewater, for this subpart, charge of process wastewater pollut- means all wastewater except for sani- ants. tary water and those wastewaters ex- § 455.65 New source performance cluded from the applicability of the standards (NSPS). rule in § 455.60. Any new source subject to this sub- § 455.62 Effluent limitations guidelines part which discharges process waste- representing the degree of effluent water pollutants must meet the fol- reduction attainable by the applica- lowing standards: There shall be no dis- tion of the best practicable pollut- charge of process wastewater pollut- ant control technology (BPT). ants. Except as provided in 40 CFR 125.30 through 125.32, any existing point § 455.66 Pretreatment standards for existing sources (PSES). -
Dicamba Emissions Under Field Conditions As Affected by Surface
Weed Technology Dicamba emissions under field conditions as www.cambridge.org/wet affected by surface condition Thomas C. Mueller1 and Lawrence E. Steckel2 1 2 Research Article Professor, Department of Plant Sciences, University of Tennessee, Knoxville, TN, USA and Professor, Department of Plant Sciences, University of Tennessee, Knoxville, TN, USA Cite this article: Mueller TC and Steckel LE (2021) Dicamba emissions under field Abstract conditions as affected by surface condition. Weed Technol. 35: 188–195. doi: 10.1017/ The evolution and widespread distribution of glyphosate-resistant broadleaf weed species cata- wet.2020.106 lyzed the introduction of dicamba-resistant crops that allow this herbicide to be applied POST to soybean and cotton. Applications of dicamba that are most cited for off-target movement Received: 15 June 2020 have occurred in June and July in many states when weeds are often in high densities and Revised: 13 July 2020 Accepted: 11 September 2020 at least 10 cm or taller at the time of application. For registration purposes, most field studies First published online: 17 September 2020 examining pesticide emissions are conducted using bare ground or very small plants. Research was conducted in Knoxville, TN, in the summer of 2017, 2018, and 2019 to examine the effect of Associate Editor: application surface (tilled soil, dead plants, green plants) on dicamba emissions under field con- Kevin Bradley, University of Missouri ditions. Dicamba emissions after application were affected by the treated surface in all years, Nomenclature: with the order from least to most emissions being dead plants < tilled soil < green plant Dicamba; cotton; Gossypium hirsutum l.; material. -
AP-42, CH 9.2.2: Pesticide Application
9.2.2PesticideApplication 9.2.2.1General1-2 Pesticidesaresubstancesormixturesusedtocontrolplantandanimallifeforthepurposesof increasingandimprovingagriculturalproduction,protectingpublichealthfrompest-bornediseaseand discomfort,reducingpropertydamagecausedbypests,andimprovingtheaestheticqualityofoutdoor orindoorsurroundings.Pesticidesareusedwidelyinagriculture,byhomeowners,byindustry,andby governmentagencies.Thelargestusageofchemicalswithpesticidalactivity,byweightof"active ingredient"(AI),isinagriculture.Agriculturalpesticidesareusedforcost-effectivecontrolofweeds, insects,mites,fungi,nematodes,andotherthreatstotheyield,quality,orsafetyoffood.Theannual U.S.usageofpesticideAIs(i.e.,insecticides,herbicides,andfungicides)isover800millionpounds. AiremissionsfrompesticideusearisebecauseofthevolatilenatureofmanyAIs,solvents, andotheradditivesusedinformulations,andofthedustynatureofsomeformulations.Mostmodern pesticidesareorganiccompounds.EmissionscanresultdirectlyduringapplicationorastheAIor solventvolatilizesovertimefromsoilandvegetation.Thisdiscussionwillfocusonemissionfactors forvolatilization.Thereareinsufficientdataavailableonparticulateemissionstopermitemission factordevelopment. 9.2.2.2ProcessDescription3-6 ApplicationMethods- Pesticideapplicationmethodsvaryaccordingtothetargetpestandtothecroporothervalue tobeprotected.Insomecases,thepesticideisapplieddirectlytothepest,andinotherstothehost plant.Instillothers,itisusedonthesoilorinanenclosedairspace.Pesticidemanufacturershave developedvariousformulationsofAIstomeetboththepestcontrolneedsandthepreferred -
Herbicidal Composition
(19) TZZ ¥ ¥_T (11) EP 2 832 223 A1 (12) EUROPEAN PATENT APPLICATION published in accordance with Art. 153(4) EPC (43) Date of publication: (51) Int Cl.: 04.02.2015 Bulletin 2015/06 A01N 47/36 (2006.01) A01N 41/10 (2006.01) A01N 43/10 (2006.01) A01N 43/40 (2006.01) (2006.01) (2006.01) (21) Application number: 13769011.1 A01N 43/70 A01N 43/80 A01N 43/824 (2006.01) A01P 13/00 (2006.01) (22) Date of filing: 29.03.2013 (86) International application number: PCT/JP2013/059673 (87) International publication number: WO 2013/147225 (03.10.2013 Gazette 2013/40) (84) Designated Contracting States: • OKAMOTO, Hiroyuki AL AT BE BG CH CY CZ DE DK EE ES FI FR GB Kusatsu-shi GR HR HU IE IS IT LI LT LU LV MC MK MT NL NO Shiga 525-0025 (JP) PL PT RO RS SE SI SK SM TR • TERADA, Takashi Designated Extension States: Kusatsu-shi BA ME Shiga 525-0025 (JP) (30) Priority: 30.03.2012 JP 2012079935 (74) Representative: Müller-Boré & Partner Patentanwälte PartG mbB (71) Applicant: Ishihara Sangyo Kaisha, Ltd. Friedenheimer Brücke 21 Osaka-shi, Osaka 550-0002 (JP) 80639 München (DE) (72) Inventors: • YAMADA, Ryu Kusatsu-shi Shiga 525-0025 (JP) (54) HERBICIDAL COMPOSITION (57) To provide a high active herbicidal composition at least one 4-hydroxyphenylpyruvate dioxygenase in- having a broad herbicidal spectrum. hibitor selected from the group consisting of sulcotrione, A herbicidal composition comprising, as active in- bicyclopyrone, mesotrione, topramezone and their salts; gredients, (a) nicosulfuron or its salt, (b) terbuthylazine and group C2 is at least one very long chain fatty acid or its salt and (c) compound C (compound C is at least biosynthesis inhibitor selected from the group consisting one herbicidal compound selected from the group con- of dimethenamid-P, flufenacet and their salts). -
Coa F128821.Pdf
page 1 of 4 Version 1 CERTIFIED REFERENCE MATERIAL Triazine & Urea Pesticide Mixture - 29 components; 100ug/ml each of Atrazine [CAS:1912-24-9] ; Atrazine-desethyl [CAS:6190-65-4] ; Atrazine-desisopropyl [CAS:1007-28-9] ; Metamitron [CAS:41394-05-2] ; Chloridazon [CAS:1698-60-8] ; Metoxuron [CAS:19937-59-8] ; Carbetamide [CAS:16118-49-3] ; Bromacil [CAS:314-40-9] ; Simazine [CAS:122-34-9] ; Cyanazine [CAS:21725-46-2] ; Terbuthylazine-desethyl [CAS:30125-63-4] ; Methabenzthiazuron [CAS:18691-97-9] ; Chlortoluron [CAS:15545-48-9] ; Monolinuron [CAS:1746-81-2] ; Diuron [CAS:330-54-1] ; Isoproturon [CAS:34123-59-6] ; Metobromuron [CAS:3060-89-7] ; Metazachlor [CAS:67129-08-2] ; Propazine [CAS:139-40-2] ; Dimefuron [CAS:34205-21-5] ; Terbuthylazine [CAS:5915-41-3] ; Linuron [CAS:330-55-2] ; Chloroxuron [CAS:1982-47-4] ; Prometryn [CAS:7287-19-6] ; Chlorpropham [CAS:101-21-3] ; Terbutryn [CAS:886-50-0] ; Metolachlor [CAS:51218-45-2] ; Ethofumesate [CAS:26225-79-6] ; Ethidimuron [CAS:30043-49-3] in Acetonitrile Lot N: XXXXXX Ref N: F128821 Certification Date:XXXXXX Barcode: XXXXXXXX Component Certified Value* CAS Chemical Formula and uncertainty [µg/ml] Atrazine 99.71 ± 1.19 1912-24-9 C8H14ClN5 Atrazine-desethyl 99.76 ± 1.88 6190-65-4 C6H10ClN5 Atrazine-desisopropyl 100.08 ± 2.34 1007-28-9 C5H8ClN5 Metamitron 99.93 ± 1.09 41394-05-2 C10H10N4O Chloridazon 99.57 ± 1.26 1698-60-8 C10H8ClN3O Metoxuron 100.01 ± 1.34 19937-59-8 C10H13ClN2O2 Carbetamide 100.00 ± 1.48 16118-49-3 C12H16N2O3 Bromacil 99.70 ± 1.17 314-40-9 C9H13BrN2O2 Simazine 100.09 ± -
12 Chemical Fact Sheets
1212 ChemicalChemical factfact sheetssheets A conceptual framework for Introduction implementing the Guidelines (Chapter 1) (Chapter 2) he background docudocu-- ments referred to in FRAMEWORK FOR SAFE DRINKING-WATER SUPPORTING Tments referred to in INFORMATION thisthis chapterchapter (as the princi-princi- Health-based targets Public health context Microbial aspects pal reference for each fact (Chapter 3) and health outcome (Chapters 7 and 11) sheet) may be found on Water safety plans Chemical aspects (Chapter 4) (Chapters 8 and 12) thethe Water, Sanitation, HyHy-- System Management and Radiological Monitoring giene and Health web site assessment communication aspects at http://www.who.int/ (Chapter 9) Acceptability Surveillance water_sanitation_health/ aspects (Chapter 5) dwq/chemicals/en/indewater-quality/guidelines/x. (Chapter 10) htmlchemicals/en/. A complete. A complete list of rlist eferences of references cited citedin this in Application of the Guidelines in specic circumstances chapter,this chapter, including including the (Chapter 6) background documents Climate change, Emergencies, Rainwater harvesting, Desalination forfor each cchemical, hemical, is pro-pro- systems, Travellers, Planes and vided in Annex 22.. ships, etc. 12.1 Chemical contaminants in drinking-water Acrylamide Residual acrylamideacrylamide monomermonomer occursoccurs inin polyacrylamidepolyacrylamide coagulantscoagulants used used in in thethe treattreat-- ment of drinking-water. In general, thethe maximummaximum authorizedauthorized dosedose ofof polymerpolymer isis 11 mg/l. mg/l. At a monomer content of 0.05%, this corresponds to a maximum theoretical concen-- trationtration ofof 0.5 µg/l of the monomer in water.water. Practical concentrations maymay bebe lowerlower byby aa factor factor of 2–3. This applies applies to to thethe anionic anionic and and non-ionic non-ionic polyacrylamides, polyacrylamides, but but residual residual levelslevels fromfrom cationic polyacrylamides maymay bebe higher.higher. -
List of Herbicide Groups
List of herbicides Group Scientific name Trade name clodinafop (Topik®), cyhalofop (Barnstorm®), diclofop (Cheetah® Gold*, Decision®*, Hoegrass®), fenoxaprop (Cheetah® Gold* , Wildcat®), A Aryloxyphenoxypropionates fluazifop (Fusilade®, Fusion®*), haloxyfop (Verdict®), propaquizafop (Shogun®), quizalofop (Targa®) butroxydim (Falcon®, Fusion®*), clethodim (Select®), profoxydim A Cyclohexanediones (Aura®), sethoxydim (Cheetah® Gold*, Decision®*), tralkoxydim (Achieve®) A Phenylpyrazoles pinoxaden (Axial®) azimsulfuron (Gulliver®), bensulfuron (Londax®), chlorsulfuron (Glean®), ethoxysulfuron (Hero®), foramsulfuron (Tribute®), halosulfuron (Sempra®), iodosulfuron (Hussar®), mesosulfuron (Atlantis®), metsulfuron (Ally®, Harmony®* M, Stinger®*, Trounce®*, B Sulfonylureas Ultimate Brushweed®* Herbicide), prosulfuron (Casper®*), rimsulfuron (Titus®), sulfometuron (Oust®, Eucmix Pre Plant®*), sulfosulfuron (Monza®), thifensulfuron (Harmony®* M), triasulfuron, (Logran®, Logran® B Power®*), tribenuron (Express®), trifloxysulfuron (Envoke®, Krismat®*) florasulam (Paradigm®*, Vortex®*, X-Pand®*), flumetsulam B Triazolopyrimidines (Broadstrike®), metosulam (Eclipse®), pyroxsulam (Crusader®Rexade®*) imazamox (Intervix®*, Raptor®,), imazapic (Bobcat I-Maxx®*, Flame®, Midas®*, OnDuty®*), imazapyr (Arsenal Xpress®*, Intervix®*, B Imidazolinones Lightning®*, Midas®*, OnDuty®*), imazethapyr (Lightning®*, Spinnaker®) B Pyrimidinylthiobenzoates bispyribac (Nominee®), pyrithiobac (Staple®) C Amides: propanil (Stam®) C Benzothiadiazinones: bentazone (Basagran®, -
US Environmental Protection Agency Office of Pesticide Programs
US Environmental Protection Agency Office of Pesticide Programs Reregistration Eligibility Decision for Prometon March 25, 2008 United States Prevention, Pesticides EPA 738-R-08-004 Environmental Protection and Toxic Substances Agency (7508P) Reregistration Eligibility Decision for Prometon TABLE OF CONTENTS GLOSSARY OF TERMS AND ABBREVIATIONS............................................................................... 4 I. INTRODUCTION.............................................................................................................................. 5 II. CHEMICAL OVERVIEW................................................................................................................ 6 A. REGULATORY HISTORY ................................................................................................................... 6 B. CHEMICAL IDENTIFICATION............................................................................................................. 6 C. USE PROFILE .................................................................................................................................... 7 D. ESTIMATED USAGE OF PESTICIDE.................................................................................................... 8 III. SUMMARY OF PROMETON RISK ASSESSMENTS............................................................. 9 A. HUMAN HEALTH RISK ASSESSMENT ............................................................................................... 9 1. Toxicity of Prometon.................................................................................................................. -
Pesticide Contamination Prevention Program Report A.R.S
Pesticide Contamination Prevention Program Report A.R.S. 49-303.C § The Arizona Pesticide Contamination Prevention Program was established by the Environmental Quality Act of 1986. The major objective of the program is to prevent or mitigate groundwater pollution by agricultural pesticides. The program is composed of the following four major components: 1) Product chemistry and environmental fate review – Prior to registering an agricultural-use pesticide with the Arizona Department of Agriculture (ADA), applicants must submit product chemistry and environmental fate data of the associated active ingredient to ADEQ for review and approval. The information is used to determine the potential of the active ingredient to leach to groundwater, and generate the Arizona Groundwater Protection List (GWPL). 2) Groundwater Protection List – The GWPL is a list of agricultural pesticides in use in Arizona and their active ingredients that have the potential to pollute groundwater, based on product chemistry and environmental fate data and groundwater monitoring of the active ingredient(s). 3) Environmental monitoring – ADEQ, in cooperation with the ADA, monitors groundwater and soils in agricultural areas throughout the state for the presence of agricultural-use pesticide active ingredients on the GWPL. 4) Compilation of data – ADEQ collects and reports product use information for agricultural pesticides applied to the soil on the GWPL. Results of pesticide monitoring for ground-water wells are evaluated and stored in the Water Quality Division’s groundwater database. This report which covers calendar year 2011 is in fulfillment of a requirement pursuant to A.R.S. § 49- 303.C that requires ADEQ to report the following information to the Legislature annually: 1) A list of agricultural-use pesticide active ingredient for which there is a groundwater protection data gap (A.R.S. -
Journal of Plant Protection Research ISSN 1427-4345
Journal of Plant Protection Research ISSN 1427-4345 ORIGINAL ARTICLE A study on Sorghum bicolor (L.) Moench response to split application of herbicides Sylwia Kaczmarek* Department of Weed Science and Plant Protection Techniques, Institute of Plant Protection – National Research Institute, Władysława Węgorka 20, 60-318 Poznań, Poland Vol. 57, No. 2: 152–157, 2017 Abstract DOI: 10.1515/jppr-2017-0021 Field experiments to evaluate the split application of mesotrione + s-metolachlor, mesot- rione + terbuthylazine, dicamba + prosulfuron, terbuthylazine + mesotrione + s-metol- Received: March 10, 2017 achlor, and sulcotrione in the cultivation of sorghum var. Rona 1 were carried out in 2012 Accepted: May 24, 2017 and 2013. Th e fi eld tests were conducted at the fi eld experimental station in Winna Góra, Poznań, Poland. Treatments with the herbicides were performed directly aft er sowing (PE) *Corresponding address: and at leaf stage 1–2 (AE1) or at leaf stage 3–4 (AE2) of sorghum. Th e treatments were car- [email protected] ried out in a laid randomized block design with 4 replications. Th e results showed that the tested herbicides applied at split doses were eff ective in weed control. Aft er the herbicide application weed density and weed biomass were signifi cantly reduced compared to the infested control. Th e best results were achieved aft er the application of mesotrione tank mixture with s-metolachlor and terbuthylazine. Application of split doses of herbicides was also correlated with the density, biomass, and height of sorghum. Key words: herbicides, mesotrione, s-metolachlor, sorghum, split doses, terbuthylazine, weed control Introduction Sorghum, the oldest cultivated crop in the world, is a total area of 390,000 ha.