SAFETY DATA SHEETS for Forestry-Labeled Herbicides
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Safety Data Sheet
SAFETY DATA SHEET 1. Product and Company Identification Product identifier SSS O3 Professional Cleaning System Other means of identification O3 Professional Cleaning System Ozonated Water Recommended use Not available. Recommended restrictions None known. Manufacturer/Importer/Supplier/Distributor information Manufacturer Company name Tersano Inc. Address 5000 Regal Drive Oldcastle, ON N0R 1A0 Canada Telephone 1-800-808-1723 (Toll-Free) Website www.tersano.com E-mail [email protected] Emergency phone number 1-800-808-1723 (Toll-Free) 2. Hazards Identification Physical hazards Not classified. Health hazards Not classified. Environmental hazards Not classified. OSHA defined hazards Not classified. Label elements Hazard symbol None. Signal word None. Hazard statement The mixture does not meet the criteria for classification. Precautionary statement Prevention Observe good industrial hygiene practices. Response Not applicable. Storage Not applicable. Disposal No special precautions required. Hazard(s) not otherwise None known. classified (HNOC) Supplemental information Not applicable. 3. Composition/Information on Ingredients Mixtures Chemical name Common name and synonyms CAS number % Water 7732-18-5 >99.99 Ozone 10028-15-6 <0.01 4. First Aid Measures Inhalation Not applicable. Skin contact Not applicable. Eye contact Not applicable. Ingestion Not applicable. Most important This material is not expected to be harmful. symptoms/effects, acute and delayed #25447 Page: 1 of 6 Issue date 17-December-2014 LBUxxx, LSRxxx, LSCxxx, LQFCxxx Indication of immediate Treat symptomatically. medical attention and special treatment needed General information Ensure that medical personnel are aware of the material(s) involved, and take precautions to protect themselves. 5. Fire Fighting Measures Suitable extinguishing media Not applicable, non-combustible. -
Exposure to Carcinogens and Work-Related Cancer: a Review of Assessment Methods
European Agency for Safety and Health at Work ISSN: 1831-9343 Exposure to carcinogens and work-related cancer: A review of assessment methods European Risk Observatory Report Exposure to carcinogens and work-related cancer: A review of assessment measures Authors: Dr Lothar Lißner, Kooperationsstelle Hamburg IFE GmbH Mr Klaus Kuhl (task leader), Kooperationsstelle Hamburg IFE GmbH Dr Timo Kauppinen, Finnish Institute of Occupational Health Ms Sanni Uuksulainen, Finnish Institute of Occupational Health Cross-checker: Professor Ulla B. Vogel from the National Working Environment Research Centre in Denmark Project management: Dr Elke Schneider - European Agency for Safety and Health at Work (EU-OSHA) Europe Direct is a service to help you find answers to your questions about the European Union Freephone number (*): 00 800 6 7 8 9 10 11 (*) Certain mobile telephone operators do not allow access to 00 800 numbers, or these calls may be billed. More information on the European Union is available on the Internet ( 48TU http://europa.euU48T). Cataloguing data can be found on the cover of this publication. Luxembourg: Publications Office of the European Union, 2014 ISBN: 978-92-9240-500-7 doi: 10.2802/33336 Cover pictures: (clockwise): Anthony Jay Villalon (Fotolia); ©Roman Milert (Fotolia); ©Simona Palijanskaite; ©Kari Rissa © European Agency for Safety and Health at Work, 2014 Reproduction is authorised provided the source is acknowledged. European Agency for Safety and Health at Work – EU-OSHA 1 Exposure to carcinogens and work-related cancer: -
Ammonia Solution.Pdf
SAFETY DATA SHEET Creation Date 23-Nov-2009 Revision Date 13-Apr-2015 Revision Number 4 SECTION 1: IDENTIFICATION OF THE SUBSTANCE/MIXTURE AND OF THE COMPANY/UNDERTAKING 1.1. Product identification Product Description: Ammonia solution 35% Cat No. : A/3240/PB15, A/3240/PB17 Molecular Formula H5 N O 1.2. Relevant identified uses of the substance or mixture and uses advised against Recommended Use Laboratory chemicals. Uses advised against No Information available 1.3. Details of the supplier of the safety data sheet Company Fisher Scientific UK Bishop Meadow Road, Loughborough, Leicestershire LE11 5RG, United Kingdom E-mail address [email protected] 1.4. Emergency telephone number Chemtrec US: (800) 424-9300 Chemtrec EU: 001 (202) 483-7616 Tel: 01509 231166 SECTION 2: HAZARDS IDENTIFICATION 2.1. Classification of the substance or mixture CLP Classification - Regulation (EC) No 1272/2008 Physical hazards Based on available data, the classification criteria are not met Health hazards Skin Corrosion/irritation Category 1 B Serious Eye Damage/Eye Irritation Category 1 Specific target organ toxicity - (single exposure) Category 3 Environmental hazards Acute aquatic toxicity Category 1 Classification according to EU Directives 67/548/EEC or 1999/45/EC Symbol(s) C - Corrosive N - Dangerous for the environment R-phrase(s) R34 - Causes burns R50 - Very toxic to aquatic organisms For the full text of the R-phrases and H-Statements mentioned in this Section, see Section 16. ______________________________________________________________________________________________ -
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®), -
Weed Control in Direct-Seeded Field Pea Gregory J
Weed Control in Direct-seeded Field Pea Gregory J. Endres and Blaine G. Schatz Weed control and field pea response to selected soil- and POST-applied herbicides were evaluated in a randomized complete-block design with three replicates. The experiment was conducted on a Heimdahl loam soil with 6.7 pH and 2.9% organic matter at the NDSU Carrington Research Extension Center. Herbicide treatments were applied to 5- by 25-ft plots with a pressurized hand-held plot sprayer at 17 gal/A and 30 psi through 8002 flat-fan nozzles. Fall sulfentrazone treatments were applied October 25, 2004 to a moist soil surface with 47 F, 71% RH, 15% clear sky, and 11 mph wind. On April 28, 2005, inoculated 'Integra' field pea was seeded into standing wheat stubble in 7-inch rows at a rate of 300,000 pure live seeds/A. PRE treatments were applied to a dry soil surface on April 30 with 31 F, 64% RH, 30% clear sky, and 10 mph wind. Rainfall totaled 1.22 inches 8 d following PRE application. The trial area was treated on May 6 with a PRE burn-down application of glyphosate at 0.75 lb ae/A plus ammonium sulfate at 1% v/v. The early POST (EPOST) treatment was applied on May 23 with 73 F, 35% RH, 100% cloudy sky, and 6 mph wind to 2-inch tall field pea, 1- to 2-leaf green and yellow foxtail, 0.5-inch tall common lambsquarters, 0.5-inch tall prostrate and redroot pigweed, and 0.5-inch tall wild buckwheat. -
Safety and Efficacy of Postemergence Herbicides for Container-Grown Landscape Groundcovers
1 17B-Student-Conner-IPPS-2018.doc Safety and Efficacy of Postemergence Herbicides for Container-Grown Landscape Groundcovers© Crystal J. Connera, Chris Marble, and Annette Chandler Mid-Florida Research and Education Center, University of Florida, 2725 S. Binion Road, Apopka, Florida 32703, USA aEmail: [email protected] KeyWords: Landscape nursery, weed management, asiatic jasmine, Trachelospermum asiaticum ‘Minima’, perennial peanut, Arachis glabrata ‘Ecoturf’ SUMMARY Research was conducted to determine crop tolerance of asiatic jasmine (Trachelospermum asiaticum ‘Minima’) and perennial peanut (Arachis glabrata ‘Ecoturf’) to postemergence herbicides including bentazon, sulfentrazone, iron HEDTA, indaziflam (a preemergence herbicide), sulfosulfuron, and clopyralid. Efficacy of these herbicides was evaluated on flowering eclipta (Eclipta prostrata) and hairy beggarticks (Bidens pilosa). All herbicides with the exception of bentazon caused no significant damage to asiatic jasmine; injury resulting from bentazon was minimal. In perennial peanut, the highest injury was noted in plants treated with indaziflam, sulfosulfuron, or clopyralid, but injury was less than 30% and considered acceptable. All herbicides evaluated provided poor control of either weed species with the exception of clopyralid, which provided over 90% control of hairy beggarticks. Results indicate that several postemergence herbicides labeled for use in either nurseries or landscapes could be used to manage weeds in asiatic jasmine or perennial peanut groundcovers but further testing is needed. 1 2 INTRODUCTION Turfgrass is the most widely planted irrigated crop in the United States and occupies the vast majority of most residential and commercial landscapes in Florida (NTRI, 2003). However, the common mantra of landscape design is “right plant right place”. In many neighborhoods, parks, and other areas containing significant tree canopy, turfgrass is not suitable due to limited sunlight. -
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. -
Use Patterns and Formulations
PESTICIDE FACT SHEET Name of Chemical: Indaziflam Reason for Issuance: Conditional Registration Date Issued: July 26, 2010 I. DESCRIPTION OF CHEMICAL Chemical Name: Indaziflam; N-[(1R,2S)-2,3-dihydro-2,6-dimethyl-1H-inden-1-yl]-6-[(1RS)-1 fluoroethyl]-1,3,5-triazine-2,4-diamine Common Name: Indaziflam EPA PC Code: 080818 Chemical Abstracts Service (CAS) Number: 950782-86-2 Year of Initial Registration: 2010 Pesticide Type: Herbicide Chemical Class: Alkylazine Mode of Action: Indaziflam controls weeds by inhibiting cellulose biosynthesis (CB Inhibitor) Registrant: Bayer Environmental Science and Bayer Advanced II. USE PATTERNS AND FORMULATIONS Application Sites: Indaziflam is a selective herbicide providing pre-emergence and post- emergence (when indaziflam is formulated with 2,4-D, dicamba, mecoprop, and penoxsulam) control of annual grasses and broadleaf weeds. Indaziflam is registered for application to residential and commercial areas (lawns, ornamentals, and hardscapes including patios, walkways, etc.), turf (parks, cemeteries, golf courses, sod farms, sports fields, and commercial lawns), field grown ornamentals and Christmas trees, commercial nursery and landscape plantings, and forestry sites. Types of Formulations: Indaziflam is registered as EPA Reg. 432-RLNR (1501) BCS AA10717 Technical Herbicide (containing 95.8% indaziflam) and EPA Reg. 432-RUOI (1498) BCS-AA10717 2% MUP Herbicide (containing 2.0% indaziflam). Indaziflam is proposed for use by commercial applicators (formulated in water soluble bags and added to turf fertilizer). These proposed registrations include EPA Reg. 432-RUOO (1499) BCS-AA10717 20WSP Herbicide (containing 20.0% indaziflam), EPA Reg. 432-RUOL (1495) BCS-AA10717 0.0142% Plus Turf Fertilizer Herbicide (containing 0.0142% indaziflam), EPA Reg. -
Pesticide and Metabolite Standards Catalog Table of Contents GENERAL INFORMATION
Pesticide and Metabolite Standards Catalog Table of Contents GENERAL INFORMATION ........................................................................................................ 2 Ordering Information Fax Order Form Making Dilutions Miscibility Table How To Read a Chem Service Label PESTICIDE AND METABOLITE STANDARDS - ALPHABETICAL LISTING .......................7 PESTICIDE STANDARDS LISTING BY CAS NUMBER WITH STRUCTURES .....................28 METABOLITE STANDARDS LISTING BY PARENT COMPOUND WITH STRUCTURES .. 161 GOVERNMENT/STATE/INTERNATIONAL AGENCY STANDARDS .................................... 178 EPA 500 .................................................................................................................................180 EPA 600 .................................................................................................................................190 EPA 1600 ...............................................................................................................................197 EPA 8000 ...............................................................................................................................199 EPA 8100 ...............................................................................................................................200 EPA 8200 ...............................................................................................................................203 EPA 8300 ...............................................................................................................................204 -
Turfgrass Science 1 Goosegrass Biology and Management in Turf Darcy E
ENH1133 Turfgrass Science 1 Goosegrass Biology and Management in Turf Darcy E. P. Telenko, Ramon G. Leon, and J. Bryan Unruh 2 Goosegrass (Eleusine indica), also known as silver Turf management practices that reduce soil compaction crabgrass or crowfoot, is a major turf weed found and excess soil moisture and that maintain healthy throughout Florida. It is a tough, clumped, dark green turf will minimize goosegrass infestation. A number of summer annual with a generally “whitish to silverish” preemergence herbicides are available for goosegrass coloration at the center of the plant. The leaf blade is control, and applications should be made in late winter smooth on both surfaces, and occasionally a few hairs or early spring when soil temperatures reach 60°F for can be found near the base on the edge of the blade. 24 consecutive hours to ensure proper placement of the It measures 0.2 to 0.4 inches wide. The visible ligule is herbicide before goosegrass germination. Postemergence short toothed and membranous. Seedhead spikelets form control is dependent on turfgrass species and requires in two rows on 2 to 13 “fingers.” Frequently, a single repeat applications of herbicides for successful finger will form below the terminal cluster of fingers. goosegrass management. Goosegrass tolerates close mowing and compacted wet or dry soils. In the spring, goosegrass germinates when soil temperatures reach 63°F–65°F for at least 24 consecutive hours. 1 This document is ENH1133, one of a series of the Environmental Horticulture Department, UF/IFAS Extension. Original publication date July 2009. Revised February 2013 and April 2016.