Characterization of Strains of Scenedesmus Resistant to the Herbicide DCMU, (3-(3,4-Dichloropheny1)-1,1-Dimethylurea)
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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. -
U.S. EPA, Pesticide Product Label, DICAMBAZINE, 09/25/2003
UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON. D.C. 20460 OFFICE OF PREVENTION, PESTICIDES AND TOXIC SUBSTANCES SEP 2 5 2003 Albaugh, Inc. clo Pyxis Regulatory Consulting, Inc. ATTN: Michael Kellogg 11324 1']'1' Ave. Ct. NW Gig Harbor, W A 98332 Dear Mr. Kellogg: Subject: Fast Track Amendment for Atrazine Product Product: Dicambaiine EPA Registration Number: 42750-41 Submission Date: 04/24/03 The labeling referred to above, submitted in connection with registration under the Federal Insecticide, Fungicide and Rodenticide Act, as amended is acceptable, provided you make the followmg changes before you release the product for shipment. 1. Change the PPE section to the following: • "Some materials that are chemical-resistant to this product are barrier laminate> 14 mils, neoprene rubber> 14 mils, polyvinyl chloride (PVC) > 14 mils, butyl rubber> 14 mils, orviton >14 mils. Ifyou want more options, follow the instructions for category A on an EPA chemical-resistance category selection chart. " • "Mixers, loaders, applicators and other handlers not using Engineering Controls must wear: Coveralls over long sleeved ~hirt and long pants Chemical resistant gloves Chemical resistant footwear plus socks Chemical resistant headgear (if overhead exposure) A NlOSH approved dust mist filtering respirator with any N, R, P or HE filter A chemical resistant apron (if exposed to undiluted product)" • "Mixers, loaders, applicators and other handlers using Engineering Controls must wear: Long-sleeved shirt and long pants Chemical resistant gloves and apron for mixers and loaders Shoes plus socks See Engineering Controls for additional requirements" Note to registrant: You must drop the N type filter from the respirator statement if the product contains or is used with oil. -
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. -
Decision Guidance Documents
OPERATION OF THE PRIOR INFORMED CONSENT PROCEDURE FOR BANNED OR SEVERELY RESTRICTED CHEMICALS IN INTERNATIONAL TRADE DECISION GUIDANCE DOCUMENTS Dinoseb and its salts and esters JOINT FAO/UNEP PROGRAMME FOR THE OPERATION OF PRIOR INFORMED CONSENT United Nations Environment Programme UNEP Food and Agriculture Organization of the United Nations OPERATION OF THE PRIOR INFORMED CONSENT PROCEDURE FOR BANNED OR SEVERELY RESTRICTED CHEMICALS IN INTERNATIONAL TRADE DECISION GUIDANCE DOCUMENTS Dinoseb and its salts and esters JOINT FAO/UNEP PROGRAMME FOR THE OPERATION OF PRIOR INFORMED CONSENT Food and Agriculture Organization of the United Nations United Nations Environment Programme Rome - Geneva 1991 DISCLAIMER The inclusion of these chemicals in the Prior Informed Consent Procedure is based on reports of control action submitted to the United Nations Environment Programme (UNEP) by participating countries, and which are presently listed in the UNEP-International Register of Potentially Toxic Chemicals (IRPTC) database on Prior Informed Consent. While recognizing that these reports from countries are subject to confirmation, the FAO/UNEP Joint Working Group of Experts on Prior Informed Consent have recommended that these chemical be included in the Procedure. The status of these chemicals will be reconsidered on the basis of such new notifications as may be made by participating countries from time to time. The use of trade names in this document is primarily intended to facilitate the correct identification of the chemical. It is not intended to imply approval or disapproval of any particular company. As it is not possible to include all trade names presently in use, only a number of commonly used and published trade names have been included here. -
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®, -
Herbicides to Isolated Thylakoid Membranes and Intact
Comparative Binding of Photosystem II — Herbicides to Isolated Thylakoid Membranes and Intact Green Algae Henrik Laasch, Klaus Pfister, and Wolfgang Urbach Botanisches Institut der Universität Würzburg, Mittlerer Dallenbergweg 64, D-8700 Würzburg, Bundesrepublik Deutschland Z. Naturforsch. 36 c, 1041-1049 (1981); received July 13, 1981 Herbicides, Herbicide Binding, Photosynthesis, Thylakoids, Algae The binding of the photosystem II herbicides diuron (DCMU), atrazine (s-triazine), ioxynil and dinoseb (substituted phenols) to isolated spinach thylakoids was saturated in less than 2 min in the dark. In intact cells of the green alga Ankistrodesmus b. it took 10 to 20 min to reach the binding equilibrium. Binding affinity of diuron, atrazine, dinoseb, measured as equilibrium binding constants, was found to be comparable in isolated thylakoids and intact algal cells. For ioxynil, reduced binding affinity was observed in algae. The concentration of binding sites in thylakoids and intact cells was determined to be 300-500 chl/inhibitor binding site, suggesting a 1:1 stoichiometry between bound herbicide and electron transport chains. In intact cells only the phenol herbicides ioxynil and dinoseb showed increased concentrations of binding sites. Strong correlation of herbicide binding and inhibition of electron transport was found for diuron in isolated thylakoids and intact cells. In thylakoids this is valid also for atrazine and dinoseb. For ioxynil a difference between the amount of binding and inhibition was found. This correlation of herbicide binding and inhibition proves that binding specifically occurs at the inhibition site at photosystem H. In addition to the specific binding, for all four herbicides studied, (except for ioxynil in thylakoids) unspecific binding was observed in thylakoids as well as in algae, which was not related to inhibition. -
Pesticide Simazine and Breast Cancer Risk
Pesticide Simazine and Breast Cancer Risk http://envirocancer.cornell.edu/Bibliography/pesticide/bib.simazine.cfm Skip to main content New Program Learning Resources Events Maps & Stats Research Resources BCERF Research Pesticide Simazine and Breast Cancer Risk Bibliography This bibliography is provided as a service to our readers. It is compiled from the entries in the BCERF Environmental Risk Factors Bibliographic Database. This bibliography is arranged topically. The topics include: Chemical Names and Trade Names Transformation Products and Metabolites History of Use and Usage Regulatory Status and Regulations Human Studies-Evidence of Carcinogenicity Animal Experimental Studies-Evidence of Carcinogencity Evidence of Estrogenicity Effect on Reproduction Formation of Co-Carcinogens Mutagenicity Environmental Fate Persistency in Soil Water Contamination Chemical Names and Trade Names Meister, R. T. (1997). Pesticide Dictionary; Simazine. In 1997 Farm Chemicals Handbook, R. T. Meister, ed. (Willoughby, OH: Meister Publishing Company), pp. C 334. Montgomery, J. H. (1993). Simazine. In Agrochemicals Desk Reference (Boca Raton: Lewis Publishers), pp. 371-377. WSSA. (1994). Simazine. In Herbicide Handbook, 7th, W. H. Ahrens, ed. (Champaign, IL: Weed Science Society of America), pp. 270-272. Transformation Products and Metabolites Adams, N. H., Levi, P., and Hodgson, E. (1990). In vitro studies of the metabolism of atrazine, simazine, and terbutryn in several vertebrate species. Journal of Agricultural and Food Chemistry 38, 1411-1417. WSSA. (1994). Simazine. In Herbicide Handbook, 7th, W. H. Ahrens, ed. (Champaign, IL: Weed Science Society of America), pp. 270-272. History of Use and Usage Bartowiak, D., Newhart, K., Pepple, M., Troiano, J., and Weaver, D. (1995). Sampling for Pesticide Residues in California Well Water; 1995 Update of the Well Inventory Data Base (Sacremento, CA: California Environmental Protection Agency, Dept. -
Pesticides EPA 738-R-06-008 Environmental Protection and Toxic Substances April 2006 Agency (7508P)
Simazine RED April 6, 2006 United States Prevention, Pesticides EPA 738-R-06-008 Environmental Protection and Toxic Substances April 2006 Agency (7508P) Reregistration Eligibility Decision for Simazine Page 1 of 266 Reregistration Eligibility Decision (RED) Document for Simazine List A Case Number 0070 Approved by: Date: April 6, 2006 Debra Edwards, Ph. D. Director Special Review and Reregistration Division Page 2 of 266 Table of Contents Simazine Reregistration Eligibility Decision Team ................................................................... 5 Glossary of Terms and Abbreviations ........................................................................................ 6 Abstract.......................................................................................................................................... 8 I. Introduction............................................................................................................................... 9 II. Chemical Overview................................................................................................................ 10 A. Chemical Identity ................................................................................................................10 B. Use and Usage Profile .........................................................................................................11 C. Tolerances............................................................................................................................12 III. Summary of Risk Assessments -
Ph DEPENDENCE of the EFFECTS of DIURON, ATRAZINE and DINOSEB on the LUMINESCENT PROPERTIES of THYLAKOID MEMBRANES
BULG. J. PLANT PHYSIOL., 2001, 27(1–2), 85–100 85 pH DEPENDENCE OF THE EFFECTS OF DIURON, ATRAZINE AND DINOSEB ON THE LUMINESCENT PROPERTIES OF THYLAKOID MEMBRANES Petar Lambrev, Vassilij Goltsev* Department of Biophysics and Radiobiology, Biological Faculty, University of Sofia “St. Kliment Ohridski” Received May 17, 2001 Summary. The effect of the external pH in the range of 5.5 to 8.0 on the activity of three PSII herbicides (diuron, atrazine and dinoseb) was studied in isolated thylakoid membranes by means of prompt and delayed fluores- cence induction kinetics. Well-expressed pH dependence was established for prompt fluorescence parameters (Fv/Fm, Fi/Fm) as well as for delayed fluores- cence parameters (I1, I2). Two types of pH dependence of the herbicide effect were observed. The apparent resistance to herbicides of the urea/triazine type (diuron and atrazine) was found to be maximal at pH 6–6.5, although the amplitude of the herbicide effect was different between diuron and atrazine. The pH dependences for thylakoids treated with the phenolic herbicide, dino- seb, showed a minimum in the herbicide effect at pH 7.5. The mechanism by which pH influences the herbicide sensitivity of thylakoid membranes is supposed to involve pH-induced conformational changes of the QB-binding site on the D1 protein of PSII, resulting in alteration of the affinity to the herbicide molecule. The conformation of the QB-site at a cer- tain pH is characterized by maximal herbicide resistance. The optimal value of pH depends on the type of herbicide, specifically the location of the H- bond between the herbicide molecule and D1. -
PB1775 Common Commercial Pre-Packaged Herbicide Mixtures
University of Tennessee, Knoxville TRACE: Tennessee Research and Creative Exchange Field & Commercial Crops UT Extension Publications 3-2008 PB1775 Common Commercial Pre-packaged Herbicide Mixtures The University of Tennessee Agricultural Extension Service Follow this and additional works at: https://trace.tennessee.edu/utk_agexcrop Part of the Plant Sciences Commons Recommended Citation "PB1775 Common Commercial Pre-packaged Herbicide Mixtures," The University of Tennessee Agricultural Extension Service, 08-0158 PB1775-2.5M-3/08 E12-5115-00-011-08, https://trace.tennessee.edu/utk_agexcrop/65 The publications in this collection represent the historical publishing record of the UT Agricultural Experiment Station and do not necessarily reflect current scientific knowledge or ecommendations.r Current information about UT Ag Research can be found at the UT Ag Research website. This Production is brought to you for free and open access by the UT Extension Publications at TRACE: Tennessee Research and Creative Exchange. It has been accepted for inclusion in Field & Commercial Crops by an authorized administrator of TRACE: Tennessee Research and Creative Exchange. For more information, please contact [email protected]. PB1775 Common Commercial Pre-packaged Herbicide Mixtures Photo courtesy of Larry Steckel Gregory Armel, Assistant Professor Weed Science — Horticulture Crops and Invasive Weeds G. Neil Rhodes, Professor Weed Science — Forage , Biofuel Crops, Tobacco and Aquatics William Klingeman, Associate Professor Nursery Production Lawrence Steckel, -
Leaching of Dinoseb and Metribuzin from Potato Fields in New Brunswick P
Leaching of dinoseb and metribuzin from potato fields in New Brunswick P. MILBURN1, H. O'NEILL2, C. GARTLEY3, T. POLLOCK2, J.E. RICHARDS1 and H. BAILEY2 1Agriculture Canada Research Station, P.O. Box 20280, Fredericton, NB, Canada E3B 4Z7; Environment Canada, Inland Waters Directorate, P.O. Box 861, Moneton, NB, Canada E1C 8N6; and JSoil and Water Section, New Brunswick Department ofAgriculture, P.O. Box 6000, Fredericton, NB, Canada E3B 5H1. Received 12 February 1990; accepted 7March 1991 Milbum, P.,O'Neill, H., Gartley, C, Pollock, T., Richards, J.E. and in Iowa and Minnesota alone. He furthernoted that pesticides Bailey, H. 1991. Leaching of dinoseb andmetribuzin from potato havebeen detected in winterand spring water samples, prior fields in New Brunswick. Can.Agric.Eng.33:197-204. Tiledrainage to new application, indicating that several pesticides are per waters from five systematically tiled, commercial potato fields in sisting in groundwater year-round. northwestern New Brunswick were analyzed for the herbicides Approximately 36 000 metric tonnes of pesticide active metribuzin and dinoseb from April 1987 to April 1989. Tile drain ingredient were sold in Canada in 1985 (Pierce and Wong outflowrate and volume were also recorded. Dinoseb and metribuzin 1988). Frank et al. (1987b) reported on sampling 359 rural were detected in tile outflow both during the year of application and during the subsequent spring melt period, butat concentrations sub wells in Ontario for suspectedpesticide contamination where stantially less than maximum acceptable concentrations (MAC) for the cited causes were spills, spray drift, or surface runoff drinking water published by Health and Welfare Canada. -
Using Countless Tons of Arsenic As a Non-Selective Contact and Soil Sterilant
87 In addition to requiring the user to obtain a permit from, the agricultural commissioner, t4e regulations prescribe certain conditions to be met by those who possess or use sodium arsenite as follows: (a) No pesticide containing sodium arsenite shall be applied on exposed vegetation (other than dormant grapeviries) unless the vegetation to be treated is enclosed within a good and su£ficient fence or otherwis.e made inaccessible to grazing animals, pets, and children. (b) No pesticide containing sodium arsenite sha,11 be applied on soil or vegetation (other than dormant grapevines) in any area penetrated by roots of any plant of value, without the written consent of the owner of such plant. ( c) No pesticide containing sodium arsenite shall be kept or placed in drinking cups, pop bottles, or other containers of a type commonly used for food or drink. (d) No pesticide containing sodium arsenite, whether in concentrated or dilute form, shall be stored, placed, or transported in any container or receptacle which does not bear on the outside a conspicuous poison label which conforms to the label required to be placed on all packages of arsenic compounds and pre:parations sold or delivered within the State. These are only procedures that any careful person would observe in the use of a poisonous material like sodium arsenite. It is just over one year since the regulations became effective. In that time we have heard of no accidental deaths involving sodium arsenite in California and the regulations appear to be serving a good purpose. SUBSTITUTE HERBICIDES FOR SODIUM ARSENITE W.