A Method for Enhancing the Rainfastness of Glyphosate
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Common and Chemical Names of Herbicides Approved by the WSSA
Weed Science 2010 58:511–518 Common and Chemical Names of Herbicides Approved by the Weed Science Society of America Below is the complete list of all common and chemical of herbicides as approved by the International Organization names of herbicides approved by the Weed Science Society of for Standardization (ISO). A sponsor may submit a proposal America (WSSA) and updated as of September 1, 2010. for a common name directly to the WSSA Terminology Beginning in 1996, it has been published yearly in the last Committee. issue of Weed Science with Directions for Contributors to A herbicide common name is not synonymous with Weed Science. This list is published in lieu of the selections a commercial formulation of the same herbicide, and in printed previously on the back cover of Weed Science. Only many instances, is not synonymous with the active ingredient common and chemical names included in this complete of a commercial formulation as identified on the product list should be used in WSSA publications. In the absence of label. If the herbicide is a salt or simple ester of a parent a WSSA-approved common name, the industry code number compound, the WSSA common name applies to the parent as compiled by the Chemical Abstracts Service (CAS) with compound only. CAS systematic chemical name or the systematic chemical The chemical name used in this list is that preferred by the name alone may be used. The current approved list is also Chemical Abstracts Service (CAS) according to their system of available at our web site (www.wssa.net). -
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®), -
Acifluorfen Sorption, Degradation, and Mobility in a Mississippi Delta Soil
Acifluorfen Sorption, Degradation, and Mobility in a Mississippi Delta Soil L. A. Gaston* and M. A. Locke ABSTRACT repulsion effects, acifluorfen is sorbed by soil or soil Potential surface water and groundwater contaminants include her- constituents (Pusino et al., 1991; Ruggiero et al., 1992; bicides that are applied postemergence. Although applied to the plant Pusino et al., 1993; Gennari et al., 1994b; NeÁgre et al., canopy, a portion of any application reaches the soil either directly 1995; Locke et al., 1997). Although the extent of sorp- or via subsequent foliar washoff. This study examined sorption, degra- tion in soil is generally proportional to OC content dation, and mobility of the postemergence herbicide acifluorfen (5-[2- (Gennari et al., 1994b; NeÁgre et al., 1995; Locke et al., chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenzoic acid) in Dundee 1997), sorption likely involves processes other than par- silty clay loam (fine-silty, mixed, thermic, Aeric Ochraqualf) taken titioning between aqueous and organic matter phases. from conventional till (CT) and no-till (NT) field plots. Homogeneous In particular, acifluorfen forms complexes with divalent surface and subsurface samples were used in the sorption and degrada- tion studies; intact soil columns (30 cm long and 10 cm diam.) were and trivalent cations (Pusino et al., 1991; Pusino et al., used in the mobility study. Batch sorption isotherms were nonlinear 1993) that may be sorbed or precipitated. Complex for- (Freundlich model) and sorption paralleled organic C (OC) content. mation and subsequent sorption may partially account All tillage by depth combinations of soil exhibited a time-dependent for increased acifluorfen sorption with decreasing soil approach to sorption equilibrium that was well described by a two- pH or increasing cation exchange capacity (Pusino et site equilibrium±kinetic model. -
Nomenclature of Commonly Available Herbicides in India
NOMENCLATURE OF COMMONLY AVAILABLE HERBICIDES IN INDIA Prior to the widespread use of chemical herbicides, mechanical control and cultural controls, such as altering soil pH, salinity, or fertility levels were used to control weeds. The first widely used herbicide was 2,4-dichlorophenoxyacetic acid, often abbreviated 2,4-D which kills many broadleaf plants while leaving grasses largely unaffected (high doses of 2,4-D at crucial growth periods can harm grass crops such as maize or cereals). The low cost of 2,4-D has led to continued usage today and it remains one of the most commonly used herbicides in the world. In 1950s triazine family of herbicides, which includes atrazine was introduced. Atrazine does not break down readily (within a few weeks) after being applied to soils of above neutral pH. Atrazine is said to have carryover, a generally undesirable property for herbicides. Glyphosate, frequently sold under the brand name Roundup, was introduced in 1974 for non- selective weed control. It is now a major herbicide in selective weed control in growing crop plants due to the development of crop plants that are resistant to it. Many modern chemical herbicides for agriculture are specifically formulated to decompose within a short period after application. This is desirable as it allows crops which may be affected by the herbicide to be grown on the land in future seasons. However, herbicides with low residual activity (i.e., that decompose quickly) often do not provide season-long weed control. List of herbicides with their common name -
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). -
R Graphics Output
Dexamethasone sodium phosphate ( 0.339 ) Melengestrol acetate ( 0.282 ) 17beta−Trenbolone ( 0.252 ) 17alpha−Estradiol ( 0.24 ) 17alpha−Hydroxyprogesterone ( 0.238 ) Triamcinolone ( 0.233 ) Zearalenone ( 0.216 ) CP−634384 ( 0.21 ) 17alpha−Ethinylestradiol ( 0.203 ) Raloxifene hydrochloride ( 0.203 ) Volinanserin ( 0.2 ) Tiratricol ( 0.197 ) trans−Retinoic acid ( 0.192 ) Chlorpromazine hydrochloride ( 0.191 ) PharmaGSID_47315 ( 0.185 ) Apigenin ( 0.183 ) Diethylstilbestrol ( 0.178 ) 4−Dodecylphenol ( 0.161 ) 2,2',6,6'−Tetrachlorobisphenol A ( 0.156 ) o,p'−DDD ( 0.155 ) Progesterone ( 0.152 ) 4−Hydroxytamoxifen ( 0.151 ) SSR150106 ( 0.149 ) Equilin ( 0.3 ) 3,5,3'−Triiodothyronine ( 0.256 ) 17−Methyltestosterone ( 0.242 ) 17beta−Estradiol ( 0.24 ) 5alpha−Dihydrotestosterone ( 0.235 ) Mifepristone ( 0.218 ) Norethindrone ( 0.214 ) Spironolactone ( 0.204 ) Farglitazar ( 0.203 ) Testosterone propionate ( 0.202 ) meso−Hexestrol ( 0.199 ) Mestranol ( 0.196 ) Estriol ( 0.191 ) 2,2',4,4'−Tetrahydroxybenzophenone ( 0.185 ) 3,3,5,5−Tetraiodothyroacetic acid ( 0.183 ) Norgestrel ( 0.181 ) Cyproterone acetate ( 0.164 ) GSK232420A ( 0.161 ) N−Dodecanoyl−N−methylglycine ( 0.155 ) Pentachloroanisole ( 0.154 ) HPTE ( 0.151 ) Biochanin A ( 0.15 ) Dehydroepiandrosterone ( 0.149 ) PharmaCode_333941 ( 0.148 ) Prednisone ( 0.146 ) Nordihydroguaiaretic acid ( 0.145 ) p,p'−DDD ( 0.144 ) Diphenhydramine hydrochloride ( 0.142 ) Forskolin ( 0.141 ) Perfluorooctanoic acid ( 0.14 ) Oleyl sarcosine ( 0.139 ) Cyclohexylphenylketone ( 0.138 ) Pirinixic acid ( 0.137 ) -
Ecological Risk Assessment for Saflufenacil
TEXT SEARCHABLE DCOUMENT 2011 UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON, D.C. 20460 OFFICE OF CEMICAL SAFETY AND POLLUTION PREVENTION PC Code: 118203 DP Barcode: 380638 and 381293 Thursday, April 07, 2011 MEMORANDUM SUBJECT: Ecological Risk Assessment for Saflufenacil Section 3 New Chemical Uses as a harvest aid on dry edible beans, dry peas, soybean, oilseeds "sunflower subgroup 20B", oilseeds "cotton subgroup 20C", and oilseeds canola "subgroup 20A". TO: Kathryn Montague, M.S., Product Manager 23 Herbicide Branch Registration Division (RD) (7505P) FROM: ~ Mohammed Ruhman, Ph.D., Agronomist 2 :4- . ""=- ........ 04!tJt! (I neith Sappington, Senior Biologist/Science Adviso~.... Vd- Environmental Risk Branch V O'f/ .../ II Environmental Fate and Effects Division (7507P) THROUGH: Mah Shamim, Ph.D., Branch Chief Environmental Risk Branch VI Environmental Fate and Effects Division (7507P) This ecological risk assessment for saflufenacil new uses is relying on the attached previous assessment (Attachment 1). As shown in the usage summary (Table 1), the single and seasonal rate, for all the crops range from 0.045 to 0.089 lbs a.i/A are within the range application rates used in exposure modeling for the 2009 Section 3 New Chemical Environmental Fate and Ecological Risk Assessment (DP Barcode 349855). Therefore, risk findings determined for the 2009 assessment may be used in the assessment for this submittal. Specifically, the 2009 assessment found no chronic risks to avian and mammalian species at an agricultural use rate 0 0.134 lb a.i.lA. Acute risks were not determined for birds and mammals since saflufenacil was not acutely toxic at the highest doses tested. -
Efficacy of Imazapic/Imazapyr and Other Herbicides in Mixtures for The
Efficacy of imazapic/imazapyr and other herbicides in mixtures for the control of Digitaria insularis prior to soybean sowing Efectividad de imazapic/imazapyr y otros herbicidas en mezclas para el control de Digitaria insularis en pre-siembra de soya Alfredo Junior Paiola Albrecht1, Leandro Paiola Albrecht1, André Felipe Moreira Silva²*, Romulo Augusto Ramos³, Everson Pedro Zeny³, Juliano Bortoluzzi Lorenzetti4, Maikon Tiago Yamada Danilussi4, and Arthur Arrobas Martins Barroso4 ABSTRACT RESUMEN Herbicide mixtures, use of multiple sites of action, and other Las mezclas entre herbicidas, el uso de múltiples sitios de acción weed management practices are necessary to avoid cases of y otras prácticas de manejo de malezas son necesarias para biotype resistance. The aim of this study was to evaluate the evitar otros casos de resistencia de biotipos. El objetivo de este efficiency of imazapic/imazapyr and other herbicides in mix- estudio fue evaluar la eficiencia de imazapic/imazapyr y otros tures to control Digitaria insularis at burndown before soybean herbicidas en mezclas para controlar Digitaria insularis en la sowing. This field research was conducted in Umuarama, State desecación antes de la siembra de soya. Esta investigación de of Parana (PR), Brazil, in the 2018/19 soybean season. The ex- campo se realizó en Umuarama, Estado de Paraná (PR), Brasil, periment was conducted in a randomized block experimental en la cosecha de soya de 2018/19. El experimento se realizó en design with four replicates and 11 treatments composed of the un diseño experimental de bloques al azar, con cuatro repe- application of glyphosate, clethodim, haloxyfop, imazapic/ ticiones y 11 tratamientos, compuestos por la aplicación de imazapyr, glufosinate, 2,4-dichlorophenoxyacetic acid (2,4-D), glifosato, cletodim, haloxifop, imazapic/imazapir, glufosinato, dicamba, triclopyr, and saflufenacil, in mixtures. -
Post-Emergence Weed Control Options in Tree Nut Orchards
Post-emergence Weed Control Options in Tree Nut Orchards Marcelo L. Moretti1, Rolando Mejorado1, Seth Watkins1, David Doll2, and Bradley D. Hanson1 1University of California, Davis, Dept. of Plant Sciences,2Cooperative Extension Merced County [email protected] Herbicides are the primary means of vegetation management in tree nut orchards in California. Among registered herbicides, post-emergence (POST) materials, like glyphosate, are the most widely used in tree crops because of low cost and broad weed control spectrum. However, herbicide resistance has compromised the efficacy of POST only herbicide programs in many parts of the state. Most cases of resistance in orchards are glyphosate-resistant hairy fleabane, horseweed, ryegrass, and junglerice. To manage resistant weed species, pre-emergence (PRE) herbicides can be applied during winter before weeds emerge; however, PRE herbicide use can be limited by cost and the need for rainfall to incorporate them. Even when PRE herbicides are used, most orchards will need a POST treatment to control weed escapes and to prepare the orchard for harvest operations. One approach to optimize control of late emerging or glyphosate-resistant weeds is to use alternate herbicides, mixtures, rates, or more appropriate application timing. The objective of this project was to evaluate POST control of hairy fleabane and yellow nutsedge with different herbicides combinations. Methods Field experiments were conducted in a three year-old almond orchard infested with hairy fleabane and yellow nutsedge. The orchard was located in a sandy soil area in Merced County, and irrigated with solid set sprinklers. The area is known to be infested with glyphosate-resistant hairy fleabane. -
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 -
Of in Partial Fulfillment of the Of
CHEMICAL SEEDBED PREPARATION FOR ZERO-TILLAGE CROP PRODUCTION A Thesi s Submitted to the Facu ltY of Graduate Studi es The Uni versi tY of Manitoba by Larry hliI Iiam TaYlor In Partial Fulfillment of the Requi rements for the Degree of I4aster of Sc i ence Department of Pl ant Science t4ay L977 ''CHEMICAL SEEDBED PREPARATION FOR ZERO-TILLAGE CROP PRODUCTION'' by LARRY IdILLIAI4 TAYLOR A rlissertation submitted to the Facutty of Craduate Studics <¡f the University of Manitoba in partial fulfillment of the roquirements of tht' degree of MASTTR OF SCIENCE @ 1977 Pernlission hus becn gr:rntcrl to th'j LIB¡ìARY OF '¡'llU l''NlvUlì- slTY oF MANtTollr\ to lctr<l or selt copics <¡f this tlissertr¡liot¡' t() thc NATIONAL LIBR^RY OF (:ANAI)A to rtlicrofilm this dissertatir.¡n and to lend or soll copics of the l'ilnl, ¿¡nd UNtvtiRSlTY MICROFILMS to publish ru übstruct of this dissertation' The ¡utl¡or reserves other ¡rublicittion rights' and neithcr the dissertttion ttor extcnsive extr cts liom it rrlay be printcd or other- wise reproduccd without thc author's wt ittctl ¡rertttissiotl' 'll ABSTRACT Taylor, Larry hli1ìiam. M'Sc., The University of Manitoba' flay , 1977 . Chemi cal Seedbed Preparati on for Zero-ti I I age Crop Productìon. Major Professor; Elmer H. Stobbe' Field trials were conducted under zero-tillage conditions to study broadspectrum annual weed control with applications of paraquat and glyphosate. Broadleaf herbicides were mixed wìth the paraquat and glyohosate treatments to find their.impact on the effectiveness and cost for chemical seedbed preparation. Excellent broadleaf annual weed control resuited when 0'28 kglha of bromoxyni 1 was added to 0'42 kg/ha of paraquat. -
Butafenacil – a New Complimentary Premix Partner for Triasulfuron Or Glyphosate for the Enhanced Knockdown and Residual Contro
Thirteenth Australian Weeds Conference Butafenacil – a new complimentary premix partner for triasulfuron or glyphosate for the enhanced knockdown and residual control of weeds in broadacre cropping situations Brett A. Davies Syngenta Crop Protection Pty. Ltd., 140–150 Bungaree Road, PO Box 249, Pendle Hill, New South Wales 2145, Australia Summary Butafenacil is a new pyrimidindione her- symptoms, however, are already observed within a few bicide released in Australia during the 2002 season hours after treatment. as a complementary component of two new products Trial work with butafenacil has been ongoing in – Logran® B-Power™ (a premix of triasulfuron and Australia since the mid 1990s. Over 100 trials have butafenacil), for the pre-emergent control of grass been conducted to investigate the complimentary activ- and broadleaf weeds in wheat, and Touchdown® B- ity of butafenacil in mixtures with either glyphosate or Power™ (a premix of glyphosate and butafenacil), for triasulfuron for pre-plant weed knockdown and in-crop the knockdown control of grass and broadleaf weeds residual weed. prior to the sowing of cereals crops. This paper provides a summary of the spectrum Effi cacy trials conducted throughout the major of activity on weeds of both Touchdown B-Power (a grain growing regions of Australia since the late premix of 5 g a.i. kg-1 of butafenacil, and 225 g a.i. 1990s have highlighted the enhanced knockdown kg-1 of glyphosate present as the isopropylamine salt control of Touchdown B-Power at rates ranging from as a suspension concentrate formulation) and Logran 184–636 g a.i. ha-1 of a wide range of both grass and B-Power (a premix of 200 g a.i.