Aquatic Plant Identification and Herbicide Use Guide
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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. -
Lake Mendota
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FSC-TPL-01-002 Application for a Derogation to Use a Highly Hazardous Pesticide
FSC-TPL-01-002 Application for a derogation to use a highly hazardous pesticide. 2,4-D, 2-ethylhexyl ester Name and contact details of SCS certification body requesting Dave Wager derogation: [email protected] 510 251-7049 To be completed at the national level Active ingredient for which derogation requested: Geographical scope of All states of USA requested derogation: Is there an accredited or preliminarily accredited FSC FSC US standard Forest Stewardship Standard applicable to the territory concerned? Requested time period for derogation: 5 years (nb Derogations shall normally be issued for a five-year period. There will be a presumption against renewal of a derogation after the expiry of the five-year period). 1. Demonstrated need Need may be demonstrated where: - The pesticide is used for protecting native species and forests against damage caused by introduced species or for protecting human health against dangerous diseases, OR - Use of the pesticide is obligatory under national laws or regulations, OR - Use of the pesticide is the only economically, environmentally, socially and technically feasible way of controlling specific organisms which are causing severe damage in natural forests or plantations in the specified country (as indicated by consideration, assessments and preferably field-trials of alternative non- chemical or less toxic pest-management methods) Explain how the proposed use complies with the specified criteria for need, including the consideration of alternatives which do not require the use of pesticides on the FSC list of ‘highly hazardous pesticides’: Overview 2,4-D ester is a selective herbicide used to control broad leaved plants such as woody species and forbs. -
Special Report 354 April 1972 Agricultural Experiment Station
ORTMAL DO ;10T REMOVE 7.9 m FILE Special Report 354 April 1972 Agricultural Experiment Station Oregon State University, Corvallis I FIELD APPLICATION OF HERBICIDES--AVOIDING DANGER TO FISH Erland T. Juntunen Department of Fisheries and Wildlife Oregon State University Corvallis, Oregon and Logan A. Norris Pacific Northwest Forestry Sciences Laboratory and Range Experiment Station Forest Service, U. S. Department of Agriculture Corvallis, Oregon April, 1972 Trade names are used in this publication solely to provide specific information. No endorsement of products is intended nor is criticism implieLl to products mentioned or omitted. Recommendations are not made concerning safe use of products nor is any guarantee or warranty of results or effects of the products intended or implied. ii Chemical weed and brush control with herbicides is an important land management practice in modern agriculture and forestry. In some cases, herbicides are applied directly to bodies of water for aquatic weed control. More commonly, herbicides are applied to lands adjacent to waterways for general weed and brush control. The responsible applicator will avoid damage to fishery resources by being fully aware of a particular herbicides potential hazard to fish. Herbicide applications should be considered hazardous to fish when there is the probability fish will be exposed to herbicide concen- trations which are harmful. This bulletin offers information that will aid in selecting the particular herbicides and formulations of least hazard to fish considering the toxicity of the herbicide and the poten- tial for its entry into streams, lakes, or ponds. Entry of Herbicides into the Aquatic Environment In aquatic weed control, the effective concentration of herbicide in the water depends on the rate of application, the rate of the spread of the chemical, the size and chemical composition of the body of water, the rate of degradation or adsorption of the chemical on sediments, and the rate of mixing of treated water with untreated water. -
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 -
Phytoplankton and Primary Production
Phytoplankton and Primary Production Phagotrophic dinoflagellates Cryptomonads & photosynthetic Chain Forming diatoms Diatoms Green algae Blue Green algae (Cyanobacteria) Anabaena Productivity: rate at which organic matter is produced Microcystis Production: Total organic matter produced Relationship Between Primary Productivity Lakes are Categorized According to their Level of and Phytoplankton Biomass (Production) Productivity or “Trophic State” More Productive For conditions in which nutrients are limited Less Productive Biomass Productivity g Carbon . m-3. day-1 (Production) Oligotrophic Mesotrophic Eutrophic g Carbon . m-3 Greater Water Clarity : 10 m Less Water Clarity: 2.5 m Less Algae : 1.7 µg/L Chl a More Algae : > 14 µg/L Chl a Lower Phosphorus : < 8 µg/L More Phosphorus: 16 µg/L time PHOSPHORUS AND CHLOROPHYLL CONCENTRATIONS AND SECCHI DISK DEPTHS CHARACTERISTIC OF THE TROPHIC CLASSIFICATION OF LAKES Phosphorus Concentrations Vary Across the Western Finger Lakes MEASURED PARAMETER Oligotrophic Mesotrophic Eutrophic Total Phosphorus (µg/L) AVG 8 26.7 84.4 Range 3.0- 17.7 10.7- 95.6 16-386 Chlorophyll a (µg/L) AVG 1.7 4.7 14.3 Range 0.3 - 4.5 3 – 11 3 – 78 Secchi Disk Depth (m) AVG 9.9 4.2 2.45 Range 5.4 - 28.3 1.5 – 8.1 0.8 – 7.0 Table I – Data from Wetzel, 1983 Source: CSLAP data Chlorophyll Concentrations Are Relatively Low In Conesus Lake Cycle of Phytoplankton Production and Biomass in Temperate Lakes Source: CSLAP data Start of Spring bloom Autumn bloom fall Summer turnover Dry Period & fallout Surface temperature in a -
TIEE Teaching Issues and Experiments in Ecology - Volume 3, April 2005
TIEE Teaching Issues and Experiments in Ecology - Volume 3, April 2005 ISSUES : DATA SET Changes in Lake Ice: Ecosystem Response to Global Change Robert E. Bohanan, Center for Biology Education, University of Wisconsin – Madison, Madison, WI 53706, [email protected] Marianne Krasny, Department of Natural Resources, Cornell University, Ithaca, NY, 14853, [email protected] Adam Welman, Center for the Environment, Cornell University, Ithaca, NY, 14853 THE ECOLOGICAL QUESTION: Is there evidence for global warming in long term data on changes in dates of ice cover in three Wisconsin Lakes? ECOLOGICAL CONTENT: Effects of climate change on ecological systems. WHAT STUDENTS DO: Students plot more than 100 years of data on dates of "ice on" and "ice off" and duration of ice cover for three Wisconsin Lakes. They examine patterns of variation at different time scales to see the importance of long-term data. SKILLS: Interpreting data, making inferences from trends or patterns in data, making spatial and temporal comparisons of ecological systems. ASSESSABLE OUTCOMES: Interpretation of data, analyzing trends and patterns in spatial and temporal data, and constructing explanations about the links between abiotic and biotic factors on ecological systems from large-scale data. SOURCE: North Temperate Lakes LTER archive (http://lterquery.limnology.wisc.edu/abstract_new.jsp?id=PHYS) TIEE, Volume 3 © 2005 - Robert E. Bohanan and the Ecological Society of America. Teaching Issues and Experiments in Ecology (TIEE) is a project of the Education and Human Resources Committee of the Ecological Society of America (http://tiee.ecoed.net). page 2 Robert E. Bohanan, Marianne Krasny, Adam Welman TIEE Volume 3, April 2005 OVERVIEW Note: the overview is written for faculty but can be used as the basis for an introduction to the data set for students. -
2021 Row Crop Plant-Back Intervals for Common Herbicides
DIVISION OF AGRICULTURE RESEARCH & EXTENSION University of Arkansas System Footnotes (continued) Authors 10 Replant only with Concep-treated or screen-treated seed. 2021 11 Needs 15 inches cumulative precipitation from application to planting rotational crop. Leah Collie, Program Associate - Weed Science 12 Needs 30 inches cumulative precipitation from application to planting rotational crop. Aaron Ross, Program Associate - Weed Science Tom Barber, Professor - Weed Science 13 Timeintervalisbasedon8oz/Aapplicationrateanddoesnotbeginuntil1inchof Row Crop Plant-Back rainfall is received. Tommy Butts, Assistant Professor - Weed Science 14If4oz/Aorlessusedand1inchofrainfall/irrigationreceivedafterapplication. Jason Norsworthy, Distinguished Professor - Weed Science 15 Days listed are based on University data and after receiving 1 inch of rainfall. 16 Enlist corn, cotton and soybeans can be planted immediately. University of Arkansas System, Division of Agriculture Intervals for 17 STS Soybeans can be planted immediately. Weed Science Program 18 Soil PH below 7.5. 19 ForNewpath/Prefaceuseratesgreaterthan8oz/Aperseason;onlysoybeansmaybe Common Herbicides planted the following year. 20 Rotation interval for soybean is 2 months where pH is less than 7.5. 21 Immediately if Poast Protected Crop. 22 If less than 15 inches of rainfall received since application, extend replant intervals to 18 months. If pH greater than 6.5, do not plant rice the following year. 23 18monthsforcottonifrateisgreaterthan5oz/AandpH>7.2. 24 Rotationtograinsorghumis18monthswhenSpartanisappliedat8oz/A. -
Weed Targeting Herbicide Management
EXTENSION EC708 Weed Targeting Herbicide Management Viacheslav I. Adamchuk, Extension Precision Agriculture Engineer Mark L. Bernards, Extension Irrigated Weed Specialist a major problem in summer annual crops like corn or George E. Meyer, Machine Vision Specialist sugarbeet may not even emerge when a winter annual Jerry A. Mulliken, Independent Crop Consultant crop like wheat is growing. RESOURCES ost producers use herbicides to manage weed Weeds exploit space not taken by the crop (inter- Minfestations. Generally, herbicides are applied row areas) and not disturbed by control methods such For more informa- at a uniform rate to the entire field. However, a as tillage or herbicides. Weeds vary in their response tion about precision uniform application may not be appropriate for all to different environmental cues and conditions that areas of a field. As precision agriculture technologies favor growth of one weed species over another. A few agriculture research, have developed, site-specific management of most studies have correlated landscape features and manage- education and dem- agricultural inputs, including herbicides, has become ment factors to the presence of weed patches. These onstration programs feasible. Differentiated application of herbicides is an characteristics include topography (or elevation), soil effective way to minimize herbicide costs, maximize pH, soil organic carbon (OC), fertility (nitrogen and at the University of weed control and prevent unnecessary environmental phosphorous), soil texture, field history, and herbicide Nebraska–Lincoln, waste. This circular provides basic guidance on site- use patterns. For example, topography, soil texture, specific weed management. and organic carbon can have a significant effect on visit the Web site at available moisture, which affects the ability of weeds http://precisionagriculture. -
CAS No.) Screening Justification Is Public Comment Now Open? CAS No
EGLE Air Quality Division (AQD) Air Toxics Screening Level Justifications (Numerically by CAS No.) Screening Justification Is Public Comment Now Open? CAS No. Chemical Name Level & Responses Info E-Mail AQD Deadline None ad acid View View Not Open for Public Comment None amyl acetate (mixture) View View Not Open for Public Comment None atlox 848 View View Not Open for Public Comment None biosam tp-1.5 View View Not Open for Public Comment None calcium chloride View View Not Open for Public Comment None epoxy resin solution View View Not Open for Public Comment None heptamethyl-1-vinyl-1,7-dichlorotetrasilazane View View Not Open for Public Comment None n-butylglucamine View View Not Open for Public Comment None n-chloro-2,6-difluorobenzamide View View Not Open for Public Comment None trichloroethylene View View Not Open for Public Comment None triethylammonium suleptanate View View Not Open for Public Comment 50-00-0 formaldehyde View View Not Open for Public Comment 50-03-3 hydrocortisone acetate View View Not Open for Public Comment 50-21-5 lactic acid View View Not Open for Public Comment 50-28-2 estradiol View View Not Open for Public Comment 50-29-3 ddt View View Not Open for Public Comment 50-32-8 benzo(a)pyrene View View Not Open for Public Comment 51-28-5 2,4-dinitrophenol View View Not Open for Public Comment 53-36-1 methyl predisolone acetate View View Not Open for Public Comment 53-70-3 dibenz(a,h)anthracene View View Not Open for Public Comment 56-23-5 carbon tetrachloride View View Not Open for Public Comment 56-49-5 3-methylcholanthrene View View Not Open for Public Comment 56-55-3 benz(a)anthracene View View Not Open for Public Comment 56-81-5 glycerol View View Not Open for Public Comment 57-11-4 stearic acid View View Not Open for Public Comment Revised Monday, September 27, 2021 Page 1 of 51 EGLE Air Quality Division (AQD) Air Toxics Screening Level Justifications (Numerically by CAS No.) Screening Justification Is Public Comment Now Open? CAS No. -
Environmental Health Criteria 39 PARAQUAT and DIQUAT
Environmental Health Criteria 39 PARAQUAT AND DIQUAT Please note that the layout and pagination of this web version are not identical with the printed version. Paraquat and diquat (EHC 39, 1984) INTERNATIONAL PROGRAMME ON CHEMICAL SAFETY ENVIRONMENTAL HEALTH CRITERIA 39 PARAQUAT AND DIQUAT This report contains the collective views of an international group of experts and does not necessarily represent the decisions or the stated policy of the United Nations Environment Programme, the International Labour Organisation, or the World Health Organization. Published under the joint sponsorship of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization World Health Orgnization Geneva, 1984 The International Programme on Chemical Safety (IPCS) is a joint venture of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization. The main objective of the IPCS is to carry out and disseminate evaluations of the effects of chemicals on human health and the quality of the environment. Supporting activities include the development of epidemiological, experimental laboratory, and risk-assessment methods that could produce internationally comparable results, and the development of manpower in the field of toxicology. Other activities carried out by the IPCS include the development of know-how for coping with chemical accidents, coordination of laboratory testing and epidemiological studies, and promotion of research on the mechanisms of the biological action of chemicals. ISBN 92 4 154099 4 The World Health Organization welcomes requests for permission to reproduce or translate its publications, in part or in full. Applications and enquiries should be addressed to the Office of Publications, World Health Organization, Geneva, Switzerland, which will be glad to provide the latest information on any changes made to the text, plans for new editions, and reprints and translations already available. -
How Herbicides Work: Biology to Application (Agdex 606-2)
How Herbicides Work Biology to Application Linda Hall Agriculture Research Division Alberta Agriculture and Rural Development Hugh Beckie Thomas M. Wolf Saskatoon Research Centre Saskatoon Research Centre Agriculture and Agri-Food Canada Agriculture and Agri-Food Canada Disclaimer While every effort has been made to ensure accuracy, Alberta Agriculture and Rural Development does not accept responsibility for errors or ommissions. It remains the responsibility of the readers to follow product information contained on the product label or package insert. The publisher, editor and all contributors to this publication cannot be held responsible for publication errors or any consequence resulting from the use of this publication. Published by: Alberta Agriculture and Rural Development Information Management 7000 - 113 Street Edmonton, Alberta Canada T6H 5T6 Editors: Chris Kaulbars and Gerard Vaillancourt Graphic Designer: John Gillmore Electronic Composition: Sherrill Strauss and J.A. Serafinchon Photographs: Beth Hoar – Alberta Agriculture and Rural Development David Wall – Agriculture and Agri-Food Canada Tom Wolf – Agriculture and Agri-Food Canada Dow AgroSciences Copyright © 1999. All rights reserved by Her Majesty the Queen in the right of Alberta. No part of this publication may be reproduced, stored in a retrieval system, or transmitted in any form or by any means, electronic, mechanical photocopying, recording, or otherwise without written permission from Information Management, Alberta Agriculture and Rural Development. Tables/chemical