Weed Control in Direct-Seeded Field Pea Gregory J
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PPO2 Mutations in Amaranthus Palmeri:Implications on Cross-Resistance
agriculture Article PPO2 Mutations in Amaranthus palmeri: Implications on Cross-Resistance Pâmela Carvalho-Moore 1,2 , Gulab Rangani 1, James Heiser 3, Douglas Findley 4, Steven J. Bowe 4 and Nilda Roma-Burgos 1,* 1 Department of Crop, Soil and Environmental Sciences, University of Arkansas, Fayetteville, AR 72704, USA; [email protected] (P.C.-M.); [email protected] (G.R.) 2 Former Cell and Molecular Biology Program, University of Arkansas, Fayetteville, AR 72704, USA 3 Fisher Delta Research Center, College of Agriculture, University of Missouri, Portageville, MO 63873, USA; [email protected] 4 BASF Corporation, Research Triangle Park, NC 27709, USA; douglas.fi[email protected] (D.F.); [email protected] (S.J.B.) * Correspondence: [email protected] Abstract: In Arkansas, resistance to protoporphyrinogen IX oxidase (PPO)-inhibiting herbicides in Amaranthus palmeri S. Wats. is mainly due to target site mutations. Although A. palmeri PPO-mutations are well investigated, the cross-resistance that each ppo mutant endows to weed populations is not yet well understood. We aimed to evaluate the response of PPO-resistant A. palmeri accessions, harboring the ppo2 mutations DG210 and G399A, to multiple PPO-inhibiting herbicides. Six resistant and one susceptible field accessions were subjected to a dose–response assay with fomesafen, and selected survivors from different fomesafen doses were genotyped to characterize the mutation profile. The level of resistance to fomesafen was determined and a cross-resistance assay was conducted with 1 Citation: Carvalho-Moore, P.; and 2 times the labeled doses of selected PPO herbicides. The accession with higher predicted dose Rangani, G.; Heiser, J.; Findley, D.; to control 50% of the population (ED50) had a higher frequency of DG210-homozygous survivors. -
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®), -
Appendix C - Wildlife 9/8/2008
INVASIVE PLANT BIOLOGICAL ASSESSMENT Umatilla and Wallowa-Whitman National Forests Appendix C - Wildlife 9/8/2008 APPENDIX C - WILDLIFE C-1 INVASIVE PLANT BIOLOGICAL ASSESSMENT Umatilla and Wallowa-Whitman National Forests Appendix C - Wildlife 9/8/2008 C-2 INVASIVE PLANT BIOLOGICAL ASSESSMENT Umatilla and Wallowa-Whitman National Forests Appendix C - Wildlife 9/8/2008 Appendix C ......................................................................................................................... 1 Wildlife ............................................................................................................................... 1 Exposure Groups for Forest Service Sensitive Wildlife ................................................. 6 Effects of the Alternatives on Sensitive Wildlife ........................................................... 7 Tables C-5 – C-13 Herbicides ................................................................................... 11 Umatilla and Wallowa-Whitman National Forest Herbicide Spray Buffers ................ 12 Aquatics............................................................................................................. 15 Wildlife .............................................................................................................. 15 Worker Health: Based on backpack spray applications. ................................. 15 Public Health: ................................................................................................... 16 Summary of Herbicide Effects to Wildlife -
INDEX to PESTICIDE TYPES and FAMILIES and PART 180 TOLERANCE INFORMATION of PESTICIDE CHEMICALS in FOOD and FEED COMMODITIES
US Environmental Protection Agency Office of Pesticide Programs INDEX to PESTICIDE TYPES and FAMILIES and PART 180 TOLERANCE INFORMATION of PESTICIDE CHEMICALS in FOOD and FEED COMMODITIES Note: Pesticide tolerance information is updated in the Code of Federal Regulations on a weekly basis. EPA plans to update these indexes biannually. These indexes are current as of the date indicated in the pdf file. For the latest information on pesticide tolerances, please check the electronic Code of Federal Regulations (eCFR) at http://www.access.gpo.gov/nara/cfr/waisidx_07/40cfrv23_07.html 1 40 CFR Type Family Common name CAS Number PC code 180.163 Acaricide bridged diphenyl Dicofol (1,1-Bis(chlorophenyl)-2,2,2-trichloroethanol) 115-32-2 10501 180.198 Acaricide phosphonate Trichlorfon 52-68-6 57901 180.259 Acaricide sulfite ester Propargite 2312-35-8 97601 180.446 Acaricide tetrazine Clofentezine 74115-24-5 125501 180.448 Acaricide thiazolidine Hexythiazox 78587-05-0 128849 180.517 Acaricide phenylpyrazole Fipronil 120068-37-3 129121 180.566 Acaricide pyrazole Fenpyroximate 134098-61-6 129131 180.572 Acaricide carbazate Bifenazate 149877-41-8 586 180.593 Acaricide unclassified Etoxazole 153233-91-1 107091 180.599 Acaricide unclassified Acequinocyl 57960-19-7 6329 180.341 Acaricide, fungicide dinitrophenol Dinocap (2, 4-Dinitro-6-octylphenyl crotonate and 2,6-dinitro-4- 39300-45-3 36001 octylphenyl crotonate} 180.111 Acaricide, insecticide organophosphorus Malathion 121-75-5 57701 180.182 Acaricide, insecticide cyclodiene Endosulfan 115-29-7 79401 -
Weed Management—Major Crops
Weed Technology 2010 24:1–5 Weed Management—Major Crops Annual Grass Control in Strip-Tillage Peanut Production with Delayed Applications of Pendimethalin W. Carroll Johnson, III, Eric P. Prostko, and Benjamin G. Mullinix, Jr.* In strip-tillage peanut production, situations occur when dinitroaniline herbicides are not applied in a timely manner. In these cases, dinitroaniline herbicides would be applied days or weeks after seeding. However, there is no information that documents the effects of delayed applications on weed control. Trials were conducted in 2004, 2005, and 2007 in Georgia to determine the weed control efficacy of delayed applications of pendimethalin in strip-tillage peanut production. Treatments included seven timings of pendimethalin application and three pendimethalin-containing herbicide combinations. Timings of application were immediately after seeding (PRE), vegetative emergence of peanut (VE), 1 wk after VE (VE+1wk), VE+2wk, VE+3wk, VE+4wk, and a nontreated control. Pendimethalin containing herbicide programs included pendimethalin plus paraquat, pendimethalin plus imazapic, and pendimethalin alone. Among the possible treatment combinations was a current producer standard timing for nonpendimethalin weed control programs in peanut, which was either imazapic or paraquat alone applied VE+3wk. Pendimethalin alone did not effectively control Texas millet regardless of time of application (69 to 77%), whereas southern crabgrass was controlled by pendimethalin alone PRE (87%). Delayed applications of pendimethalin controlled Texas millet and southern crabgrass when combined with either paraquat or imazapic, with imazapic being the preferred combination due to better efficacy on southern crabgrass than paraquat at most delayed applications. Peanut yield was improved when any of the herbicide combinations were applied PRE compared to later applications. -
RR Program's RCL Spreadsheet Update
RR Program’s RCL Spreadsheet Update March 2017 RR Program RCL Spreadsheet Update DNR-RR-052e The Wisconsin DNR Remediation and Redevelopment Program (RR) has updated the numerical soil standards in the August 2015 DNR-RR- 052b RR spreadsheet of residual contaminant levels (RCLs). The RCLs were determined using the U.S. EPA RSL web- calculator by accepting EPA exposure defaults, with the exception of using Chicago, IL, for the climatic zone. This documentThe U.S. provides EPA updateda summary its Regionalof changes Screening to the direct-contact Level (RSL) RCLs website (DC-RCLs) in June that2015. are To now reflect in the that March 2017 spreadsheet.update, the The Wisconsin last page ofDNR this updated document the has numerical the EPA exposuresoil standards, parameter or residual values usedcontaminant in the RCL levels calculations. (RCLs), in the Remediation and Redevelopment program’s spreadsheet of RCLs. This document The providesU.S. EPA a RSL summary web-calculator of the updates has been incorporated recently updated in the Julyso that 2015 the spreadsheet.most up-to-date There toxicity were values no changes for chemi - cals madewere certainlyto the groundwater used in the RCLs,RCL calculations. but there are However, many changes it is important in the industrial to note that and the non-industrial web-calculator direct is only a subpartcontact of the (DC) full RCLsEPA RSL worksheets. webpage, Tables and that 1 andthe other 2 of thissubparts document that will summarize have important the DC-RCL explanatory changes text, generic tablesfrom and the references previous have spreadsheet yet to be (Januaryupdated. -
US EPA, Pesticide Product Label, A335.06,09/21/2020
[Note to reviewer: [Text] in brackets denotes optional or explanatory language [Note to reviewer: {Text} in braces denotes where in the final label text will appear {BOOKLET FRONT PANEL LANGUAGE} S-METOLACHLOR GROUP 15 HERBICIDE METRIBUZIN GROUP 5 HERBICIDE FOMESAFEN GROUP 14 HERBICIDE A335.06[™] [Alternate Brand Name: Statler] [Herbicide for preemergent control of certain grasses and broadleaf weeds in Soybeans] ACTIVE INGREDIENTS: (% by weight) S-Metolachlor*………………………………………….……………………………………………………………………………..…………………… 36.29% Metribuzin**………………………………………….……………………………………………………………………………..………………………. 8.05% Fomesafen***………………………………………….……………………………………………………………………………..……………………... 7.16% OTHER INGREDIENTS: ……………………………………………………..…………………………………………………………………………….. 48.5% TOTAL …………………………………………………………………………………………………………….……………………………………………. 100.0% *contains 3.39 Ib of S-metolachlor per gallon **contains 0.75 Ib of metribuzin per gallon ***contains 0.67 Ib of fomesafen acid per gallon KEEP OUT OF REACH OF CHILDREN CAUTION Si usted no entiende la etiqueta, busque a alguien para que se la explique a usted en detalle. (If you do not understand the label, find someone to explain it to you in detail.) See [below] [inside label booklet] for [additional] [First Aid,] [Precautionary Statements] and [Directions for Use]. EPA Reg. No.: 91234-201 EPA Est. No.: Net Weight: Manufactured for: Atticus, LLC 5000 CentreGreen Way, Suite 100 Cary, NC 27513 1 {LANGUAGE INSIDE BOOKLET} FIRST AID If on skin or Take off contaminated clothing. clothing: Rinse skin immediately with plenty of water for 15-20 minutes. Call a poison control center or doctor for treatment advice. If swallowed: Call a poison control center or doctor immediately for treatment advice. Have person sip a glass of water if able to swallow. Do not induce vomiting unless told to do so by the poison control center or doctor. -
Multiple Resistance to Glyphosate, Paraquat and Accase
Research Article Received: 5 September 2017 Revised: 16 October 2017 Accepted article published: 26 October 2017 Published online in Wiley Online Library: 8 December 2017 (wileyonlinelibrary.com) DOI 10.1002/ps.4774 Multiple resistance to glyphosate, paraquat and ACCase-inhibiting herbicides in Italian ryegrass populations from California: confirmation and mechanisms of resistance Parsa Tehranchian,a* Vijay Nandula,b Mithila Jugulam,c Karthik Puttac and Marie Jasieniuka Abstract BACKGROUND: Glyphosate, paraquat and acetyl CoA carboxylase (ACCase)-inhibiting herbicides are widely used in California annual and perennial cropping systems. Recently, glyphosate, paraquat, and ACCase- and acetolactate synthase (ALS)-inhibitor resistance was confirmed in several Italian ryegrass populations from the Central Valley of California. This research characterized the possible mechanisms of resistance. RESULTS: Multiple-resistant populations (MR1, MR2) are resistant to several herbicides from at least three modes of action. Dose–response experiments revealed that the MR1 population was 45.9-, 122.7- and 20.5-fold, and the MR2 population was 24.8-, 93.9- and 4.0-fold less susceptible to glyphosate, sethoxydim and paraquat, respectively, than the susceptible (Sus) population. Accumulation of shikimate in Sus plants was significantly greater than in MR plants 32 h after light pretreatments. Glyphosate resistance in MR plants was at least partially due to Pro106-to-Ala and Pro106-to-Thr substitutions at site 106 of 5-enolpyruvylshikimate-3-phosphate synthase (EPSPS). EPSPS gene copy number and expression level were similar in plants from the Sus and MR populations. An Ile1781-to-Leu substitution in ACCase gene of MR plants conferred a high level of resistance to sethoxydim and cross-resistance to other ACCase-inhibitors. -
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 -
CLARC Excerpt
Washington State Department of Ecology - CLARC Air Table (Methods B and C) - February 2021 February 2021 S S CPFi S CPFo S Air Air RfC o RfDi o Inhalation RfDo o Oral o Air Air Method C Method C Inhalation u Inhalation IUR u Cancer Oral u Cancer u Method B Method B Noncancer Cancer Reference Reference Inhalation Potency Reference Potency Noncancer Cancer (Eq. 750-1 (Eq. 750-2 Chemical Data Links to r r r r Concentration c Dose Unit Risk c Factor Dose c Factor c (Eq. 750-1) (Eq. 750-2) adjusted) adjusted) 3 3 -1 CAS No. Group Chemical Name Important Notes (mg/m ) e (mg/kg-day) (µg/m ) e (kg-day/mg) (mg/kg-day) e (kg-day/mg) e (µg/m³) (µg/m³) (µg/m³) (µg/m³) 83-32-9 PAHs acenaphthene 6.00E-02 I 30560-19-1 Pesticides acephate 1.20E-03 O 75-07-0 VOCs acetaldehyde 9.00E-03 I 2.57E-03 2.20E-06 I 7.70E-03 4.10E+00 1.10E+00 9.00E+00 1.10E+01 34256-82-1 Pesticides acetochlor 2.00E-02 I 67-64-1 VOCs acetone 3.10E+01 A 8.86E+00 9.00E-01 I 1.40E+04 3.10E+04 75-86-5 VOCs acetone cyanohydrin 2.00E-03 X 5.71E-04 9.10E-01 2.00E+00 75-05-8 VOCs acetonitrile 6.00E-02 I 1.71E-02 2.70E+01 6.00E+01 98-86-2 SVOCs acetophenone 1.00E-01 I 62476-59-9 Herbicides acifluorfen, sodium 1.30E-02 I 107-02-8 VOCs acrolein 2.00E-05 I 5.71E-06 5.00E-04 I 9.10E-03 2.00E-02 79-06-1 VOCs acrylamide 6.00E-03 I 1.71E-03 1.00E-04 I-M 3.50E-01 2.00E-03 I 5.00E-01 I-M 2.70E+00 6.60E-03 6.00E+00 2.50E-01 79-10-7 VOCs acrylic acid 1.00E-03 I 2.86E-04 5.00E-01 I 4.60E-01 1.00E+00 107-13-1 VOCs acrylonitrile 2.00E-03 I 5.71E-04 6.80E-05 I 2.38E-01 4.00E-02 A 5.40E-01 I 9.10E-01 3.70E-02 -
Nozzle Selection and Adjuvant Impact on the Efficacy of Glyphosate And
agronomy Article Nozzle Selection and Adjuvant Impact on the Efficacy of Glyphosate and PPO-Inhibiting Herbicide Tank-Mixtures Jesaelen G. Moraes 1,* , Thomas R. Butts 1 , Vitor M. Anunciato 2 , Joe D. Luck 3 , Wesley C. Hoffmann 4, Ulisses R. Antuniassi 5 and Greg R. Kruger 1 1 Department of Agronomy and Horticulture, University of Nebraska-Lincoln, North Platte, NE 69101, USA; [email protected] (T.R.B.); [email protected] (G.R.K.) 2 Department of Plant Protection, Sao Paulo State University, Botucatu, SP 18618687, Brazil; [email protected] 3 Department of Biological System Engineering, University of Nebraska-Lincoln, North Platte, NE 69101, USA; [email protected] 4 USDA-ARS Aerial Application Technology Research Unit, College Station, TX 77845, USA; [email protected] 5 Department of Rural Engineering, Sao Paulo State University, Botucatu, SP 18618687, Brazil; [email protected] * Correspondence: [email protected]; Tel.: +1-402-219-1674 Abstract: PPO-inhibiting herbicides in combination with glyphosate for postemergence applications is a common approach to manage glyphosate- and ALS-inhibitor-resistant weeds. PPO-inhibitors can reduce glyphosate translocation when applied in tank-mixtures, but adjuvants may be used to overcome this effect. Additionally, optimal droplet size may be affected by tank-mixtures of different Citation: Moraes, J.G.; Butts, T.R.; herbicides and it can be crucial to herbicide efficacy. Field and greenhouse studies were conducted M. Anunciato, V.; Luck, J.D.; to investigate the impact of nozzle selection and adjuvants on weed control and interactions when Hoffmann, W.C.; Antuniassi, U.R.; applying PPO-inhibitors (fomesafen or lactofen) alone or in tank-mixture with glyphosate to five Kruger, G.R. -
Use of Mesotrione for Annual Bluegrass (Poa Annua L.) at Cool
USE OF MESOTRIONE FOR ANNUAL BLUEGRASS (POA ANNUA L.) AT COOL- SEASON TURFGRASS ESTABLISHMENT by KATELYN A. VENNER A Thesis submitted to the Graduate School-New Brunswick Rutgers, The State University of New Jersey in partial fulfillment of the requirements for the degree of Master of Science Graduate Program in Plant Biology written under the direction of Stephen E. Hart Ph.D. and approved by ________________________ ________________________ ________________________ New Brunswick, New Jersey October, 2011 ABSTRACT OF THE THESIS USE OF MESOTRIONE AT COOL-SEASON TURFGRASS ESTABLISMENT By Katelyn Anne Venner Thesis director: Stephen E. Hart Annual bluegrass is a problematic weed in highly maintained turfgrass environments, and is difficult to control due to its adaptability to highly maintained turfgrass environments and lack of highly effective chemical control options. Mesotrione is a relatively new herbicide which has been found to show some level of control of annual bluegrass, and is safe to use at cool season turfgrass establishment. Thus, mesotrione has potential to be utilized for weed control in cultivated sod production. The objectives of this research were to evaluate mesotrione to determine: 1) tolerance of selected tall fescue cultivars, an important turfgrass species cultivated for sod, to applications of mesotrione; 2) the length of residual of mesotrione versus prodiamine, bensulide and dithiopyr for control of annual bluegrass; and 3) potential of mesotrione to control winter annual broadleaf weeds at Kentucky bluegrass establishment. Tall fescue cultivars were found to be tolerant to mesotrione applications made preemergence and preemergence plus 4 weeks after emergence at higher rates than required for weed control.