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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®), -
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. -
ACTION: Original DATE: 08/20/2020 9:51 AM
ACTION: Original DATE: 08/20/2020 9:51 AM TO BE RESCINDED 3745-100-10 Applicable chemicals and chemical categories. [Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see paragraph (FF) of rule 3745-100-01 of the Administrative Code titled "Referenced materials."] The requirements of this chapter apply to the following chemicals and chemical categories. This rule contains three listings. Paragraph (A) of this rule is an alphabetical order listing of those chemicals that have an associated "Chemical Abstracts Service (CAS)" registry number. Paragraph (B) of this rule contains a CAS registry number order list of the same chemicals listed in paragraph (A) of this rule. Paragraph (C) of this rule contains the chemical categories for which reporting is required. These chemical categories are listed in alphabetical order and do not have CAS registry numbers. (A) Alphabetical listing: Chemical Name CAS Number abamectin (avermectin B1) 71751-41-2 acephate (acetylphosphoramidothioic acid o,s-dimethyl ester) 30560-19-1 acetaldehyde 75-07-0 acetamide 60-35-5 acetonitrile 75-05-8 acetophenone 98-86-2 2-acetylaminofluorene 53-96-3 acifluorfen, sodium salt [5-(2-chloro-4-(trifluoromethyl)phenoxy)-2- 62476-59-9 nitrobenzoic acid, sodium salt] acrolein 107-02-8 acrylamide 79-06-1 acrylic acid 79-10-7 acrylonitrile 107-13-1 [ stylesheet: rule.xsl 2.14, authoring tool: RAS XMetaL R2_0F1, (dv: 0, p: 185720, pa: -
Acute Toxicity of Atrazine, Endosulfan Sulphate and Chlorpyrifos
Bull Environ Contam Toxicol (2008) 81:485–489 DOI 10.1007/s00128-008-9517-3 Acute Toxicity of Atrazine, Endosulfan Sulphate and Chlorpyrifos to Vibrio fischeri, Thamnocephalus platyurus and Daphnia magna, Relative to Their Concentrations in Surface Waters from the Alentejo Region of Portugal P. Palma Æ V. L. Palma Æ R. M. Fernandes Æ A. M. V. M. Soares Æ I. R. Barbosa Received: 28 September 2007 / Accepted: 20 August 2008 / Published online: 8 September 2008 Ó Springer Science+Business Media, LLC 2008 Abstract Ecotoxicological effects of the herbicide atra- the herbicide atrazine are three of the pesticides most fre- zine and the insecticides endosulfan sulphate and chlor- quently used in Alentejo region crops. These compounds pyrifos were evaluated using a test battery comprising were chosen taking in account their concentration in the aquatic organisms from different trophic levels. According surface water of Alentejo region, mainly in Guadiana River, to the categories established in the EU legislation, atrazine and their environmental significance. The herbicide atrazine can be considered non-harmful for the species tested, while may reach values above maximum admissible concentration the insecticides can be considered very toxic for the crus- (MAC) allowed by Portuguese Legislation for surface taceans. The results of acute toxicity tests showed that the waters (Decreto-Lei n8236/98 1998). Despite that, atrazine sensitivity of organisms were as follows: Thamnocephalus did not pose a significant threat to the aquatic environment. platyurus [ Daphnia magna [ Vibrio fischeri. Chlorpyri- However, Solomon et al. (1996) cautioned that, when atra- fos may act as a toxic compound in the aquatic environment zine is retained in small, standing-water reservoirs or has of Guadiana River, as it may be detected in water at levels repeated inputs to a reservoir, damage can occur in the that promote toxic effects. -
The Effects of Estrogen in Atrazine-Mediated Foxp3 Induction and Inhibition of Cd4+ T Effector Cells
University of Montana ScholarWorks at University of Montana Graduate Student Theses, Dissertations, & Professional Papers Graduate School 2014 THE EFFECTS OF ESTROGEN IN ATRAZINE-MEDIATED FOXP3 INDUCTION AND INHIBITION OF CD4+ T EFFECTOR CELLS Tiffany Emmons The University of Montana Follow this and additional works at: https://scholarworks.umt.edu/etd Let us know how access to this document benefits ou.y Recommended Citation Emmons, Tiffany, "THE EFFECTS OF ESTROGEN IN ATRAZINE-MEDIATED FOXP3 INDUCTION AND INHIBITION OF CD4+ T EFFECTOR CELLS" (2014). Graduate Student Theses, Dissertations, & Professional Papers. 4350. https://scholarworks.umt.edu/etd/4350 This Thesis is brought to you for free and open access by the Graduate School at ScholarWorks at University of Montana. It has been accepted for inclusion in Graduate Student Theses, Dissertations, & Professional Papers by an authorized administrator of ScholarWorks at University of Montana. For more information, please contact [email protected]. THE EFFECTS OF ESTROGEN IN ATRAZINE-MEDIATED FOXP3 INDUCTION AND INHIBITION OF CD4+ T EFFECTOR CELLS By TIFFANY ROSE EMMONS B.S. Biology, University of California, Merced, Merced, California, 2012 Thesis presented in partial fulfillment of the requirements for the degree of Master of Science in Cellular, Molecular and Microbial Biology Option: Immunology The University of Montana Missoula, MT Official Graduation Date: July 2014 Approved by: J. B. Alexander Ross, Dean of The Graduate School Graduate School Dr. Scott Wetzel, Chair Division of Biological Sciences Dr. Stephen Lodmell Division of Biological Sciences Dr. David Shepherd Department of Biomedical and Pharmaceutical Sciences Emmons, Tiffany, M.S. Summer 2014 Biology The Effects of Estrogen in Atrazine-mediated Foxp3 Induction and Inhibition of CD4+ T effector Cells Atrazine (ATR) is a chlorotriazine herbicide that is heavily used in agricultural areas. -
What's the Deal with Andropause?
What’sF.A.Q. the Deal Troches and Bio-Identical With HormonesAndropause? Compounding Without WrittenWritten and Edited ByBy CompromiseCompounding Since Without 1962 LisaLisa Everett Everett Andersen, Andersen, B.Sc B.Sc Pharm, Pharm, CCN, CCN, FACA, FACA FIACP Compromise Since 1962 and Shana Curtis Webb, Pharm Tech In the beginning, it can be difficult to recognize and easily and Dobs of Johns Hopkins University recommend that dismissed. It might start with lowered immune function, elderly men with symptoms of hypogonadism and a total Whatmaybe aIs little a Troche irritability? and unexplainable fatigue, or perhaps testosteroneOther Dosage level of Forms 300ng/dl or less should start hormone difficulty sleeping. Slowly, the symptoms can increase and A troche is a French dosage form that dissolves between the replacement.Besides troches, But dosagewhat about forms young for hormones men with include those sameoral others appear, including hair loss, depression, the typical levels? They are also being told by their physicians that upper cheek and gum, allowing the medication to absorb tablets and capsules, sublingual lozenges, topical creams and actions of a “mid-life crisis,” and erectile dysfunction. This their lab values are in range and therefore just fine. After directly into the blood stream. Born out of the need to address ointments, suppositories, pessaries, injections, implanted cascade of events is often due to andropause (AKA the “male all, testosterone is now a controlled substance and some the problems associated with other dosage forms, troches pellets, and patches. menopause” or hypogonadism). It is the decline of androgens, practitioners don’t want to go there unless they have to. -
Impact of Atrazine on Organophosphate Insecticide Toxicity
Environmental Toxicology and Chemistry, Vol. 19, No. 9, pp. 2266±2274, 2000 q 2000 SETAC Printed in the USA 0730-7268/00 $9.00 1 .00 IMPACT OF ATRAZINE ON ORGANOPHOSPHATE INSECTICIDE TOXICITY JASON B. BELDEN and MICHAEL J. LYDY* Department of Biological Sciences, 1845 N Fairmount, Wichita State University, Wichita, Kansas 67260-0026, USA (Received 9 August 1999; Accepted 24 January 2000) AbstractÐAcute toxicity of selected organophosphorus insecticides (OPs; chlorpyrifos, methyl parathion, diazinon, and malathion) was determined for individual OPs and binary combinations of the OPs with atrazine to larvae of the midge Chironomus tentans. Atrazine individually was not acutely toxic even at high concentrations (10,000 mg/L); however, the presence of atrazine at much lower concentrations (40±200 mg/L) increased the toxicity of chlorpyrifos, methyl parathion, and diazinon. Atrazine did not increase the toxicity of malathion. Possible mechanisms for the synergistic toxicity found between atrazine and chlorpyrifos were investigated, including increased uptake rate and increased biotransformation into a more toxic metabolite. Although the uptake rate was increased by more than 40%, the resulting increase in toxicity would be minimal as compared to the 400% decrease estimated to occur in EC50 values for the same atrazine exposure (200 mg/L). Body residue analysis of midges exposed in vivo to atrazine and chlorpyrifos mixtures for 96 h indicated that a larger amount of metabolites was generated in atrazine treatments as compared to controls. Additionally, in vitro assays of microsomal proteins obtained from treated and control midges indicated that an increase in toxic metabolite (chlorpyrifos-O-analog) was generated in atrazine-treated midges. -
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 -
Cascade Range
United States bepartment of Agriculture Herbicide Forest Service Pacific Northwest Forest and Range and Conifer Experiment Station Research Paper PNW-292 Options for Reforesting October, 1981 Upper Slopes in the Cascade Range Edward J. Dimock II ROCKY Mof 'NTATN STATION This publication reports research involving pesticides. It does not contain recommendations for their use, nor does it imply that the uses discussed have been registered. All uses of pesticides must be registered by appropriate State and/or Federal agencies before they can be recommended. CAUTION: Pesticides can be injurious to humans, domestic animals, desirable Author plants, and fish or other wildlife -- if they I~ m w ~llmml are not handled or applied properly. Use EDWARD J. DIMOCK II is principal all pesticides selectively and carefully. silviculturist, Forestry Sciences Follow recommended practices for the Laboratory, 3200 Jefferson Way, disposal of surplus pesticides and Corvallis, Oregon 97331. pesticide containers. Abstract Summary Dimock, Edward J. I1. Herbicide and Nine herbicides (asulam, atrazine, Similar survival increases were also conifer options for reforesting upper bromacil, cyanazine, dalapon, consistently achieved with atrazine + slopes in the Cascade Range. Res. glyphosate, hexazinone, pronamide, and dalapon mixtures. Most successful Pap. PNW-292. Portland, OR: U.S. terbacil) were evaluated for control of applications of mixture produced 3-year Department of Agriculture, Forest sedge (Carex spp.) and beargrass survival of 62, 77, and 14 percent for white Service, Pacific Northwest Forest (Xerophyllum tenax [Pursh] Nutt.) to aid pine at the same three localities above. and Range Experiment Station; establishment of newly planted seedlings Survival of other conifers resulting from 1981.14 p. -
Weed Control Guide for Ohio, Indiana and Illinois
Pub# WS16 / Bulletin 789 / IL15 OHIO STATE UNIVERSITY EXTENSION Tables Table 1. Weed Response to “Burndown” Herbicides .............................................................................................19 Table 2. Application Intervals for Early Preplant Herbicides ............................................................................... 20 Table 3. Weed Response to Preplant/Preemergence Herbicides in Corn—Grasses ....................................30 WEED Table 4. Weed Response to Preplant/Preemergence Herbicides in Corn—Broadleaf Weeds ....................31 Table 5. Weed Response to Postemergence Herbicides in Corn—Grasses ...................................................32 Table 6. Weed Response to Postemergence Herbicides in Corn—Broadleaf Weeds ..................................33 2015 CONTROL Table 7. Grazing and Forage (Silage, Hay, etc.) Intervals for Herbicide-Treated Corn ................................. 66 OHIO, INDIANA Table 8. Rainfast Intervals, Spray Additives, and Maximum Crop Size for Postemergence Corn Herbicides .........................................................................................................................................................68 AND ILLINOIS Table 9. Herbicides Labeled for Use on Field Corn, Seed Corn, Popcorn, and Sweet Corn ..................... 69 GUIDE Table 10. Herbicide and Soil Insecticide Use Precautions ......................................................................................71 Table 11. Weed Response to Herbicides in Popcorn and Sweet Corn—Grasses -
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®,