Trifluralin Human Health and Ecological Risk Assessment FINAL REPORT

Total Page:16

File Type:pdf, Size:1020Kb

Trifluralin Human Health and Ecological Risk Assessment FINAL REPORT SERA TR-052-26-03a Trifluralin Human Health and Ecological Risk Assessment FINAL REPORT Submitted to: Paul Mistretta, COR USDA/Forest Service, Southern Region 1720 Peachtree RD, NW Atlanta, Georgia 30309 USDA Forest Service Contract: AG-3187-C-06-0010 USDA Forest Order Number: AG-43ZP-D-10-0010 SERA Internal Task No. 52-26 Submitted by: Patrick R. Durkin Syracuse Environmental Research Associates, Inc. 8125 Solomon Seal Manlius, New York 13104 E-Mail: [email protected] Home Page: www.sera-inc.com September 20, 2011 Table of Contents LIST OF FIGURES ...................................................................................................................... vii LIST OF TABLES ........................................................................................................................ vii LIST OF APPENDICES .............................................................................................................. viii LIST OF ATTACHEMENTS ...................................................................................................... viii ACRONYMS, ABBREVIATIONS, AND SYMBOLS ................................................................ ix COMMON UNIT CONVERSIONS AND ABBREVIATIONS .................................................. xii CONVERSION OF SCIENTIFIC NOTATION ......................................................................... xiii EXECUTIVE SUMMARY ......................................................................................................... xiv 1. INTRODUCTION ...................................................................................................................... 1 2. PROGRAMS DESCRIPTION ................................................................................................... 3 2.1. Overview .............................................................................................................................. 3 2.2. Chemical Description and Commercial Formulations ......................................................... 3 2.3. Application Methods ............................................................................................................ 5 2.4. Mixing and Application Rates ............................................................................................. 6 2.5. Use Statistics ........................................................................................................................ 6 3. HUMAN HEALTH .................................................................................................................... 8 3.1. HAZARD IDENTIFICATION .......................................................................................... 8 3.1.1. Overview ....................................................................................................................... 8 3.1.2. Mechanism of Action .................................................................................................... 8 3.1.3. Pharmacokinetics and Metabolism ............................................................................... 9 3.1.3.1. General Considerations .......................................................................................... 9 3.1.3.2. Dermal Absorption............................................................................................... 11 3.1.3.2.1. First-Order Dermal Absorption..................................................................... 11 3.1.3.2.2. Zero-Order Dermal Absorption .................................................................... 13 3.1.3.3. Excretion .............................................................................................................. 14 3.1.4. Acute Oral Toxicity .................................................................................................... 15 3.1.5. Subchronic or Chronic Systemic Toxic Effects .......................................................... 17 3.1.6. Effects on Nervous System ......................................................................................... 19 3.1.7. Effects on Immune System ......................................................................................... 20 3.1.8. Effects on Endocrine System ...................................................................................... 21 3.1.9. Reproductive and Developmental Effects .................................................................. 22 3.1.9.1. Developmental Studies ........................................................................................ 22 3.1.9.2. Reproduction Studies ........................................................................................... 23 3.1.10. Carcinogenicity and Mutagenicity ............................................................................ 23 3.1.11. Irritation and Sensitization (Effects on the Skin and Eyes) ...................................... 24 3.1.12. Systemic Toxic Effects from Dermal Exposure ....................................................... 24 3.1.13. Inhalation Exposure .................................................................................................. 25 3.1.14. Adjuvants and Other Ingredients .............................................................................. 25 ii 3.1.15. Impurities and Metabolites ....................................................................................... 27 3.1.15.1. Metabolites ......................................................................................................... 27 3.1.15.2. Impurities ........................................................................................................... 28 3.1.16. Toxicological Interactions ........................................................................................ 29 3.2. EXPOSURE ASSESSMENT .......................................................................................... 30 3.2.1. Overview ..................................................................................................................... 30 3.2.2. Workers ....................................................................................................................... 31 3.2.2.1. General Exposures ............................................................................................... 31 3.2.2.2. Accidental Exposures........................................................................................... 32 3.2.3. General Public ........................................................................................................... 34 3.2.3.1. General Considerations ........................................................................................ 34 3.2.3.1.1. Likelihood and Magnitude of Exposure ....................................................... 34 3.2.3.1.2. Summary of Assessments ............................................................................. 34 3.2.3.2. Direct Spray ......................................................................................................... 35 3.2.3.3. Dermal Exposure from Contaminated Vegetation ............................................... 35 3.2.3.4. Contaminated Water ............................................................................................ 35 3.2.3.4.1. Accidental Spill ............................................................................................. 35 3.2.3.4.2. Accidental Direct Spray/drift for a Pond or Stream ...................................... 36 3.2.3.4.3. Gleams-Driver Modeling .............................................................................. 36 3.2.3.4.3.1. Inputs to Gleams-Driver ........................................................................ 36 3.2.3.4.3.2. Results from Gleams-Driver .................................................................. 38 3.2.3.4.4. Other Modeling Efforts ................................................................................. 39 3.2.3.4.5. Monitoring Data ............................................................................................ 40 3.2.3.4.5.1. Monitoring Studies Involving Defined Applications ............................. 40 3.2.3.4.5.1. Other Monitoring Data ........................................................................... 41 3.2.3.4.6. Concentrations in Water Used for Risk Assessment .................................... 42 3.2.3.5. Oral Exposure from Contaminated Fish .............................................................. 43 3.2.3.5.1. Bioconcentration ........................................................................................... 44 3.2.3.5.2. Consumption of Wild-Caught Fish ............................................................... 46 3.2.3.5.3. Accidental Exposure Scenarios ..................................................................... 46 3.2.3.6. Dermal Exposure from Swimming in Contaminated Water ................................ 47 3.2.3.6. Oral Exposure from Contaminated Vegetation.................................................... 48 3.3. DOSE-RESPONSE ASSESSMENT ................................................................................. 51 3.3.1. Overview ..................................................................................................................... 51 3.3.2. Acute RfD ................................................................................................................... 51 iii 3.3.3. Chronic RfD ................................................................................................................ 52 3.3.4.
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]
  • 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®),
    [Show full text]
  • Exposure to Herbicides in House Dust and Risk of Childhood Acute Lymphoblastic Leukemia
    Journal of Exposure Science and Environmental Epidemiology (2013) 23, 363–370 & 2013 Nature America, Inc. All rights reserved 1559-0631/13 www.nature.com/jes ORIGINAL ARTICLE Exposure to herbicides in house dust and risk of childhood acute lymphoblastic leukemia Catherine Metayer1, Joanne S. Colt2, Patricia A. Buffler1, Helen D. Reed3, Steve Selvin1, Vonda Crouse4 and Mary H. Ward2 We examine the association between exposure to herbicides and childhood acute lymphoblastic leukemia (ALL). Dust samples were collected from homes of 269 ALL cases and 333 healthy controls (o8 years of age at diagnosis/reference date and residing in same home since diagnosis/reference date) in California, using a high-volume surface sampler or household vacuum bags. Amounts of agricultural or professional herbicides (alachlor, metolachlor, bromoxynil, bromoxynil octanoate, pebulate, butylate, prometryn, simazine, ethalfluralin, and pendimethalin) and residential herbicides (cyanazine, trifluralin, 2-methyl-4- chlorophenoxyacetic acid (MCPA), mecoprop, 2,4-dichlorophenoxyacetic acid (2,4-D), chlorthal, and dicamba) were measured. Odds ratios (OR) and 95% confidence intervals (CI) were estimated by logistic regression. Models included the herbicide of interest, age, sex, race/ethnicity, household income, year and season of dust sampling, neighborhood type, and residence type. The risk of childhood ALL was associated with dust levels of chlorthal; compared to homes with no detections, ORs for the first, second, and third tertiles were 1.49 (95% CI: 0.82–2.72), 1.49 (95% CI: 0.83–2.67), and 1.57 (95% CI: 0.90–2.73), respectively (P-value for linear trend ¼ 0.05). The magnitude of this association appeared to be higher in the presence of alachlor.
    [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]
  • Sorption of Atrazine, Alachlor and Trifluralin from Water Onto Different Geosorbents
    RSC Advances Sorption of atrazine, alachlor and trifluralin from water onto different geosorbents Journal: RSC Advances Manuscript ID: RA-ART-04-2014-003886.R1 Article Type: Paper Date Submitted by the Author: 04-Dec-2014 Complete List of Authors: Leovac, Anita; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Vasyukova, Ekaterina; Technische Universität Dresden, Faculty of Environmental Sciences, Institute of Urban Water Management Ivančev-Tumbas, Ivana; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Uhl, Wolfgang; Technische Universität Dresden, Faculty of Environmental Sciences, Institute of Urban Water Management Kragulj, Marijana; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Trickovic, Jelena; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Kerkez, Đurña; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Dalmacija, Bozo; University of Novi Sad Faculty of Sciences, Department for Chemistry, Biochemistry and Environmental Protection Page 1 of 21 RSC Advances 1 Sorption of atrazine, alachlor and trifluralin from water onto different geosorbents 2 Anita S. Leovac 1, Ekaterina Vasyukova 2, Ivana I. Ivan čev-Tumbas 1, Wolfgang Uhl 2, 3 Marijana M. Kragulj 1, Jelena S. Tri čkovi ć1, Đur đa V. Kerkez 1, Božo D. Dalmacija 1
    [Show full text]
  • Herbicide Programs for Managing Glyphosate- Resistant Palmer Amaranth and Common Waterhemp in Louisiana Corn, Cotton and Soybean
    Herbicide Programs for Managing Glyphosate- Resistant Palmer Amaranth and Common Waterhemp in Louisiana Corn, Cotton and Soybean Palmer amaranth and common waterhemp are extremely troublesome weeds in corn, cotton and soybean. They have the potential to • LOUISIANA PARISHES WITH substantially reduce crop yield and harvesting GLYPHOSATE-RESISTANCE • Red parishes efficiency. Glyphosate-resistant Palmer amaranth – Palmer amaranth and common waterhemp were documented • Orange parishes in Louisiana in 2010 and 2015, respectively. – common waterhemp Currently, Palmer amaranth has spread to essentially all crop-producing parishes in Louisiana, while glyphosate-resistant common waterhemp has only been documented in two parishes. Utilization of herbicides with differing modes of action (how they kill) for soil residual activity is vital for management of these two pigweed species. In addition, these herbicides typically need to be applied multiple times during the growing season. It is very important to control glyphosate-resistant Palmer amaranth and common waterhemp at germination or before they reach 3 inches in height. Timely applications are crucial because control with many herbicides is poor if they are applied after glyphosate-resistant Palmer amaranth height is taller than 3 inches. In addition to use of herbicides with differing modes of action, herbicide rotation in conjugation with crop rotation is a good way to avoid and/or manage glyphosate-resistant Palmer amaranth - female plant inflorescence Palmer amaranth. For example, if a corn and cotton rotation is used, herbicides with identical modes of action use in both crops should be applied sparingly. The same can be applied to corn/soybean or cotton/soybean rotations. It is important to also remember that numerous herbicides have a rotation interval restriction for a following crop.
    [Show full text]
  • 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
    [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]
  • Quinclorac Absorption and Translocation Characteristics in Quinclorac- and Propanil-Resistant and -Susceptible Barnyardgrass (Echinochloa Crus-Galli ) Biotypes
    Weed Technology 2007 21:683–687 Quinclorac Absorption and Translocation Characteristics in Quinclorac- and Propanil-Resistant and -Susceptible Barnyardgrass (Echinochloa crus-galli ) Biotypes M. L. Lovelace, R. E. Talbert, R. E. Hoagland, and E. F. Scherder* Studies were initiated to evaluate absorption, translocation, and distribution of 14C-quinclorac in propanil- and quinclorac-resistant (R-BYG) and -susceptible (S-BYG) barnyardgrass. No differential absorption of 14C-quinclorac was observed between R-BYG and S-BYG, but more 14C remained in the treated leaf of S-BYG (57% of total absorbed) compared with the R-BYG leaf (34% of total absorbed) at 72 h after treatment (HAT). After 12 HAT, 20 and 15% of the amount absorbed had been translocated basipetally by R-BYG and S-BYG, respectively. At 72 HAT, 27 and 17% of the total absorbed 14C had been translocated acropetally by R-BYG and S-BYG, respectively. The levels of 14C above the treated leaf continued to increase throughout the duration of the experiment in R-BYG while levels of 14C above the treated leaf in S-BYG remained relatively constant. Seven percent more of the total absorbed 14C was exuded from roots of R-BYG than S-BYG at 72 HAT. Although differential translocation was observed between R-BYG and S-BYG, it is unclear whether this difference is a cause of quinclorac resistance or an effect of some other physiological process. Further research is needed to determine if differential translocation is due to metabolism or other physiological factors. Nomenclature: Quinclorac; barnyardgrass, Echinochloa crus-galli (L.) Beauv. ECHCG.
    [Show full text]
  • Control of Crabgrass in Home Lawns
    AY-10-W IL-IN TW 33 CControlontrol ooff CrabgrassCrabgrass inin HomeHome LawnsLawns Crabgrass is a common weed that infests home lawns in the Midwest (Figure 1). Crabgrass is an summer annual weed that germinates when soil temperatures are approximately 60º F for 3-5 days at the 1/4” level. It begins fl owering and setting seed in July and dyes with the fi rst frost of fall. Crabgrass has tremendous survival reproductive Purdue University capabilities. Because of this, it is unrealistic Turf Science to expect a crabgrass free lawn. You cannot Department of eradicate crabgrass (or any other pest for that Agronomy matter); a few crabgrass plants in your lawn are Figure 1. Mature crabgrass plant (Zac Reicher). www.agry.purdue.edu/turf acceptable. Cultural Crabgrass Control The most effective way to control crabgrass is University of Illinois to create a dense, healthy turf. A healthy turf will Turfgrass Program compete well with crabgrass and prevent it from Department of establishing. Natural Mowing Resources and Environmental • Mow at 2.5 to 3.0 inches depending on the turf Sciences species. Mowing below this range will increase www.turf.uiuc.edu crabgrass populations (Figure 2). • Mow frequently so as not to remove more than Figure 2. High crabgrass population in a Kentucky 1/3 of the leaf blade at one time. This may mean bluegrass lawn mown at 1.0 inch (Aaron Patton). mowing twice weekly in spring and every other week in summer. Fertilization Irrigation Apply 2 to 4 pounds nitrogen per 1000 ft2 each Irrigate deeply and infrequently.
    [Show full text]
  • 400 Part 180—Tolerances And
    Pt. 180 40 CFR Ch. I (7–1–11 Edition) (iv) The data and information sub- 180.4 Exceptions. mitted in support of the petition. 180.5 Zero tolerances. (v) The notice of filing of the peti- 180.6 Pesticide tolerances regarding milk, tion. eggs, meat, and/or poultry; statement of policy. (3) Any order issued under § 180.29(f) of this chapter to which the objection Subpart B—Procedural Regulations related, the regulation that was the subject of that order, and each related 180.7 Petitions proposing tolerances or ex- Notice of Proposed Rulemaking. emptions for pesticide residues in or on raw agricultural commodities or proc- (4) The comments submitted by mem- essed foods. bers of the public in response to the 180.8 Withdrawal of petitions without preju- Notice of Filing or Notice of Proposed dice. Rulemaking, and the information sub- 180.9 Substantive amendments to petitions. mitted as part of the comments, the 180.29 Establishment, modification, and rev- Administrator’s response to comments ocation of tolerance on initiative of Ad- and the documents or information re- ministrator. lied on by the Administrator in issuing 180.30 Judicial review. 180.31 Temporary tolerances. the regulation or order. 180.32 Procedure for modifying and revoking (5) All other documents or informa- tolerances or exemptions from toler- tion submitted to the docket for the ances. rulemaking in question under parts 177 180.33 Fees. or part 180 of this chapter. 180.34 Tests on the amount of residue re- (6) The Notice of Hearing published maining. under § 179.20.
    [Show full text]