The Persistence, Degradation, and Mobility of Metolachlor in Soil And

Total Page:16

File Type:pdf, Size:1020Kb

The Persistence, Degradation, and Mobility of Metolachlor in Soil And Iowa State University Capstones, Theses and Retrospective Theses and Dissertations Dissertations 1996 The persistence, degradation, and mobility of metolachlor in soil and the fate of metolachlor and atrazine in surface water, surface water/sediment, and surface water/aquatic plant systems Pamela Joan Rice Iowa State University Follow this and additional works at: https://lib.dr.iastate.edu/rtd Part of the Agriculture Commons, Environmental Sciences Commons, Fresh Water Studies Commons, and the Soil Science Commons Recommended Citation Rice, Pamela Joan, "The persistence, degradation, and mobility of metolachlor in soil and the fate of metolachlor and atrazine in surface water, surface water/sediment, and surface water/aquatic plant systems " (1996). Retrospective Theses and Dissertations. 11405. https://lib.dr.iastate.edu/rtd/11405 This Dissertation is brought to you for free and open access by the Iowa State University Capstones, Theses and Dissertations at Iowa State University Digital Repository. It has been accepted for inclusion in Retrospective Theses and Dissertations by an authorized administrator of Iowa State University Digital Repository. For more information, please contact [email protected]. INFORMATION TO USERS This manuscript has been reproduced from the microfilm master. UMI films the text directly from the original or copy submitted. Thus, some thesis and dissertation copies are in typewriter face, while others may be from any type of computer printer. The quality of this reproduction is dependent upon the quality of the copy submitted. Broken or indistinct print, colored or poor quality illustrations and photographs, print bleedthrough, substandard margins, and improper alignment can adversely affect reproduction. In the unlikely event that the author did not send UMI a complete manuscript and there are missing pages, these will be noted. Also, if unauthorized copyright material had to be removed, a note will indicate the deletion. Oversize materials (e.g., maps, drawings, charts) are reproduced by sectioning the original, beginning at the upper left-hand comer and continuing from left to right in equal sections with small overlaps. Each original is also photographed in one exposure and is included in reduced form at the back of the book. Photographs included in the original manuscript have been reproduced xerographically in this copy. Higher quality 6" x 9" black and white photographic prints are available for any photographs or illustrations appearing in this copy for an additional charge. Contact UMI directly to order. UMI A Bell & Howell Information Company 300 Notth Zsdb Road, Ann Aibor MI 48106-1346 USA 313/761-4700 800/521-0600 The persistence, d^radation, and mobility of metolachlor in soil and the fiite of metolachlor and atrazine in surface water, surface water/sediment, and surface water/aquatic plant systems by Pamela Joan Rice A dissertation submitted to the graduate faculty in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY Major: Toxicology Major Professors: Joel R. Coats and Todd A. Anderson Iowa State University Ames, Iowa 1996 UMI Number: 9712595 UMI Microform 9712595 Copyright 1997, by UMI Company. All rights reserved. This microform edition is protected against unauthorized copying under Title 17, United States Code. UMI 300 North Zeeb Road Ann Arbor, MI 48103 ii Graduate College Iowa State University This is to certify that the Doctoral dissertation of Pamela Joan Rice has met the dissertation requirements of Iowa State University Signature was redacted for privacy. Signature was redacted for privacy. Co-major Professor Signature was redacted for privacy. For the-Major Program Signature was redacted for privacy. iii TABLE OF CONTENTS LIST OF FIGURES v LIST OF TABLES ix CHAPTER 1. GENERAL INTRODUCTION 1 Introduction 1 Metolachlor; Use I Metolachlor: D^radation 2 Metolachlor: Mobility in Soil 5 Herbicide Contamination of Surface Water 6 Persistence of Metolachlor and Atrazine in Water 8 Problems Associated with Pesticide-Contaminated Water 9 Remediation of Contaminated Water with Aquatic Plants 11 Dissertation Objectives 12 Dissertation Organization 14 CHAPTER 2. THE INFLUENCE OF SOIL MOISTURE AND HERBICIDE CONCENTRATION ON THE DEGRADATION OF METOLACHLOR IN SURFACE AND SUBSURFACE SOILS 16 Abstiract 16 Introduction 17 Materials and Methods 18 Results 24 Discussion 38 Acknowledgments 40 References 41 CHAPTER 3. MOBILITY AND PERSISTENCE OF METOLACHLOR IN UNDISTURBED SOIL COLUMNS 44 Abstract 44 Introduction 45 Materials and Methods 47 Results and Discussion 52 Conclusion 58 Acknowledgment 60 Referoices 60 iv CHAPTER 4. FATE OF METOLACHLOR AND ATRAZINE IN SURFACE WATER AND SURFACE WATER/SEDIMENT INCUBATION SYSTEMS 64 Abstract 64 Introduction 65 Matmals and Methods 65 Results 69 Discussion 86 Conclusion 89 Acknowledgment 89 References 90 CHAPTER 5. PHYTOREMEDIATION OF HERBICIDE-CONTAMINATED WATER WITH AQUATIC PLANTS 93 Abstract 93 Introduction 94 Materials and Methods 96 Results 100 Discussion 117 Acknowledgments 120 Refoences 120 GENERAL CONCLUSIONS 125 Environmental Fate of Metolachlor in Soil 125 Persistence of Metolachlor and Atrazine in Surface Water and the Remediation of Herbicide-Contaminated Water with Aquatic Plants 126 GENERAL REFERENCES 127 ACKNOWLEDGMENTS 133 V LIST OF FIGURES CHAPTER 1. GENERAL INTRODUCTION Figure L Metolachlor and metolachlor degradation products 3 Figure!. Atrazine and atrazine degradation products 10 CHAPTER 2. THE INFLUENCE OF SOIL MOISTURE AND HERBICIDE CONCENTRATION ONTHE DEGRADATION OF METOLACHLOR IN SURFACE AND SUBSURFACE SOILS Figure 1. Metolachlor and its carbinol (CGA-40172) and morpholinone (CGA-40919) metabolites 19 Figure2. Fate of ['"Clmetolachlor in surface (0-30 cm) and subsurface (90-120 cm) soils at two soil moistures (unsaturated (-0.3 bar, -33 ld>a) and saturated (30% above -0.3 bar)). The dissipation of metolachlor (panel A), formation of nonextractable residues (panel B) and the formation of extractable degradation products (panel C) were determined by thin layer chromatography and soil combustion as described in the materials and methods. Abbreviations: 30 = 0-30 cm; 120 = 90-120 cm; U = unsaturated; S = saturated 26 Figure 3. Figure 3. Fate of ["C]metolachlor in sterile and nonsterile surface (0-30 cm) and subsurface (90-120 cm) soils at two soil moistures [unsaturated (-0.3 bar, -33 kPa) and saturated (30% above -0.3 bar)]. The dissipation of metolachlor (panels A&D), formation of nonextractable residues (panels B&E) and the formation of extractable degradation products (panels C&F) were determined by thin-layer chromatography and soil combustion as described in the Materials and Methods. Abbreviations: 30 = 0-30 cm; 120 = 90-120 cm; NS = nonsterile; ST = sterile (autoclaved for 1 hour at 121°C for two consecutive days); U = unsaturated; S = saturated 31 Figure 4. Fate of ['''C]metolachlor in surface (0-30 cm) and subsurface (90-120 cm) soils at two soil moistures [unsaturated (-0.3 bar, -33 kPa) and saturated (30% above -0.3 bar)] and two herbicide concentrations (9 |ig/g and 90 ^g/g). The dissipation of metolachlor (panels A&D), formation of nonextractable residues (panels B&£) and the formation of extractable degradation products (panels C&F) were determined by thin-layer chromatography and soil combustion as described in the Materials and Methods. Abbreviations; 30 = 0-30 cm; 120 = 90-120 cm; U = unsaturated; S = saturated 34 vi Figure S. Microbial respiration in metolachlor-treated surface soils(0-30 cm) 36 Figure 6. Microbial respiration in metolachlor-treated subsurface soils (90-120 cm) 37 CHAPTER 3. MOBILITY AND PERSISTENCE OF METOLACHLOR IN UNDISTURBED SOIL COLUMNS Figure I. Undisturbed soil column 49 Figure 2. Distribution of '"C in the leached soil column 53 Figure 3. Quantity of metolachlor and metolachlor degradation products detected in the soil extracts of the leached soil column 57 Figure 4. Metolachlor and metolachlor degradation products in the leachate of the soil columns 59 CHAPTER 4. FATE OF METOLACHLOR AND ATRAZINE IN SURFACE WATER AND SURFACE WATER/SEDIMENT INCUBATION SYSTEMS Figure 1. Percentage of applied ['^C]metolachlor remaining in the water of the surface water and surface water/sediment incubation system after 60 days 74 Figure 2. Percentage of applied ['"HDJatrazine remaining in the water of the surface water and surface water/sediment incubation system after 60 days 75 Figure 3. Distribution of'"C and [''*C]metolachIor in the surface water (nonsterile)/sediment (nonsterile) incubation systems. (''KH-MET = ["C]metolachlor, sed. = sediment) 76 Figure 4. Distribution of and ['''CJmetolachlor in the surface water (sterile)/sediment (sterile) incubation systems. ('"'C-MET = ["C]metolachlor, sed. = sediment; sterile = autoclaved for 1 h at 120°C for two consecutive days) 77 Figure 5. Distribution of and ["Cjatrazine in the surface water (nonsterile)/sediment (nonsterile) incubation systems. ("'C-ATR= ['"CJatrazine; sed. = sediment) 78 vii Figure 6. Distribution ofand [''*C]atrazine in the sur&ce water (sterile)/sediment (sterile) incubation systems. ('^-ATR = ["C]atrazine; sed. = sediment; sterile = autoclaved for 1 h at 120°C for two consecutive days) 79 CHAPTERS. PHYTOREMEDIATION OF HERBICIDE-CONTAMINATED WATER WITH AQUATIC PLANTS Figure 1. Percentage of applied ['"^jmetolachlor remaining in the water of the nonvegetated- and vegetated-surface water incubation systems after 16 days 101 Figure 2. Percentage of applied ['"Cjatrazine remaining in the water of the nonvegetated-
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]
  • Corn and Soybean Mode of Action Herbicide Chart
    By Premix Corn and Soybean This chart lists premix herbicides alphabetically by their trade names so you can identify the premix’s component herbicides and their respective site of action groups. Refer Herbicide Chart to the Mode of Action chart for more information. Component Repeated use of herbicides with the same Site of Premix Trade Active Action site of action can result in the development of Trade Name ® Name ® Ingredient Group* herbicide-resistant weed populations. Authority First ............... Spartan sulfentrazone 14 FirstRate cloransulam 2 Axiom ........................... Define flufenacet 15 This publication was designed for commercial printing, color shifts may occur on other printers and on-screeen. Sencor metribuzin 5 Basis . ........................... Resolve rimsulfuron 2 Harmony GT thifensulfuron 2 By Mode of Action (effect on plant growth) Bicep II Magnum .......... Dual II Magnum s-metolachlor 15 AAtrex atrazine 5 This chart groups herbicides by their modes of action to assist Bicep Lite II Magnum .... Dual II Magnum s-metolachlor 15 AAtrex atrazine 5 you in selecting herbicides 1) to maintain greater diversity in Boundary ...................... Dual Magnum s-metolachlor 15 herbicide use and 2) to rotate among herbicides with different Sencor metribuzin 5 Breakfree ATZ ............... Breakfree acetochlor 15 sites of action to delay the development of herbicide resistance. atrazine atrazine 5 Breakfree ATZ Lite ........ Breakfree acetochlor 15 Number of atrazine atrazine 5 resistant weed Buctril + Atrazine ......... Buctril bromoxynil 6 atrazine atrazine 5 species in U.S. Bullet ............................ Micro-Tech alachlor 15 Site of Chemical Active atrazine atrazine 5 Action Product Examples Camix ........................... Callisto mesotrione 28 Group* Site of Action Family Ingredient (Trade Name ®) Dual II Magnum s-metolachlor 15 Lipid Canopy DF ..................
    [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]
  • U.S. Geological Survey National Water-Quality Assessment Program
    U.S. Geological Survey National Water-Quality Assessment Program Stream water-quality analytes Major ions and trace elements­schedule 998 (20 constituents) Pesticides ­­schedule 2437 (229 compounds) Alkalinity 1H­1,2,4­Triazole Arsenic 2,3,3­Trichloro­2­propene­1­sulfonic acid (TCPSA) Boron 2,4­D Calcium 2­(1­Hydroxyethyl)­6­methylaniline Chloride 2­[(2­Ethyl­6­methylphenyl)amino]­1­propanol Fluoride 2­Amino­N­isopropylbenzamide Iron 2­Aminobenzimidazole Lithium 2­Chloro­2',6'­diethylacetanilide 2­Chloro­4,6­diamino­s­triazine {CAAT} Magnesium (Didealkylatrazine) pH 2­Chloro­4­isopropylamino­6­amino­s­triazine Potassium 2­Chloro­6­ethylamino­4­amino­s­triazine {CEAT} Total dissolved solids 2­Chloro­N­(2­ethyl­6­methylphenyl)acetamide Selenium 2­Hydroxy­4­isopropylamino­6­amino­s­triazine 2­Hydroxy­4­isopropylamino­6­ethylamino­s­triazin Silica e {OIET} Sodium 2­Hydroxy­6­ethylamino­4­amino­s­triazine Specific conductance 2­Isopropyl­6­methyl­4­pyrimidinol Strontium 3,4­Dichlorophenylurea Sulfate 3­Hydroxycarbofuran Turbidity 3­Phenoxybenzoic acid Vanadium 4­(Hydroxymethyl)pendimethalin 4­Chlorobenzylmethyl sulfoxide Suspended sediment 4­Hydroxy molinate 4­Hydroxychlorothalonil Nutrients­schedule 2430 (18 constituents) 4­Hydroxyhexazinone A Inorganic carbon, suspended Acephate Dissolved inorganic carbon Acetochlor ammonia + organic nitrogen (unfiltered­Kjeldahl) Acetochlor oxanilic acid ammonia + organic nitrogen (filtered­Kjeldahl) Acetochlor sulfonic acid Ammonia as N, filtered Acetochlor sulfynilacetic acid nitrite, filtered 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]
  • Jamesdanieljonesiiithesis.Doc-After Defense
    The Evaluation of HPPD-Inhibitors for Full-Season Control of Morningglory (Ipomoea) Species in Corn (Zea mays L.) by James Daniel Jones III A thesis submitted to the Graduate Faculty of Auburn University in partial fulfillment of the requirements for the Degree of Master of Science Auburn, Alabama December 15, 2018 Keywords: Ipomoea, corn, HPPD, postemergence Approved by Dr. Dennis Delaney, Chair, Extension Specialist, Crop, Soil, and Environmental Sciences Dr. Andrew Price, Affiliate Associate Professor, Crop, Soil, and Environmental Sciences Dr. Audrey Gamble, Assistant Professor and Extension Specialist, Crop, Soil, and Environmental Sciences i Abstract Due to late-season morningglory harvest interference concerns in corn, field studies were conducted in 2017 and 2018 at the Prattville Agricultural Research Unit in Prattville, Alabama and at the Sand Mountain Research and Extension Center in Crossville, Alabama to evaluate late season control of morningglory species using HPPD- inhibitors postemergence (POST) applied alone, following atrazine preemergence (PRE), or in combination with atrazine. Additionally, Amaranthus spp. and Senna spp. were evaluated for control. An incomplete randomized design with a split-plot treatment arrangement with four replications was utilized. The trial was divided into two sections: one with a PRE application of atrazine and a second without a preemergence application of atrazine. Eleven herbicides were applied POST without atrazine including: tembotrione; mesotrione; topramezone+dimethenamid; mesotrione+S- metolachlor+glyphosate; tembotrione+thiencarbazone; topramezone; mesotrione+S- metolachlor+atrazine; mesotrione+S-metolachlor+atrazine+bicyclopyrone; mesotrione+nicosulfuron; isoxaflutole; isoxaflutole+thiencarbazone-methyl; non-treated with atrazine applied PRE, and a true non-treated check. The same herbicides, excluding the two treatments that contain atrazine in the premixture, were also applied with atrazine.
    [Show full text]
  • Pesticide Trends in Major Rivers of the United States, 1992–2010
    National Water-Quality Assessment Program Pesticide Trends in Major Rivers of the United States, 1992–2010 Scientific Investigations Report 2014–5135 U.S. Department of the Interior U.S. Geological Survey Cover. View of Missouri River from Double Ditch Indian Village Historic Site, north of Bismarck, North Dakota, September 26, 2006 (photograph by Kathleen Macek-Rowland). Pesticide Trends in Major Rivers of the United States, 1992–2010 By Karen R. Ryberg, Aldo V. Vecchia, Robert J. Gilliom, and Jeffrey D. Martin National Water-Quality Assessment Program Scientific Investigations Report 2014–5135 U.S. Department of the Interior U.S. Geological Survey U.S. Department of the Interior SALLY JEWELL, Secretary U.S. Geological Survey Suzette M. Kimball, Acting Director U.S. Geological Survey, Reston, Virginia: 2014 For more information on the USGS—the Federal source for science about the Earth, its natural and living resources, natural hazards, and the environment, visit http://www.usgs.gov or call 1–888–ASK–USGS. For an overview of USGS information products, including maps, imagery, and publications, visit http://www.usgs.gov/pubprod To order this and other USGS information products, visit http://store.usgs.gov Any use of trade, firm, or product names is for descriptive purposes only and does not imply endorsement by the U.S. Government. Although this information product, for the most part, is in the public domain, it also may contain copyrighted materials as noted in the text. Permission to reproduce copyrighted items must be secured from the copyright owner. Suggested citation: Ryberg, K.R., Vecchia, A.V., Gilliom, R.J., and Martin, J.D., 2014, Pesticide trends in major rivers of the United States, 1992–2010: U.S.
    [Show full text]
  • 12 Chemical Fact Sheets
    1212 ChemicalChemical factfact sheetssheets A conceptual framework for Introduction implementing the Guidelines (Chapter 1) (Chapter 2) he background docudocu-- ments referred to in FRAMEWORK FOR SAFE DRINKING-WATER SUPPORTING Tments referred to in INFORMATION thisthis chapterchapter (as the princi-princi- Health-based targets Public health context Microbial aspects pal reference for each fact (Chapter 3) and health outcome (Chapters 7 and 11) sheet) may be found on Water safety plans Chemical aspects (Chapter 4) (Chapters 8 and 12) thethe Water, Sanitation, HyHy-- System Management and Radiological Monitoring giene and Health web site assessment communication aspects at http://www.who.int/ (Chapter 9) Acceptability Surveillance water_sanitation_health/ aspects (Chapter 5) dwq/chemicals/en/indewater-quality/guidelines/x. (Chapter 10) htmlchemicals/en/. A complete. A complete list of rlist eferences of references cited citedin this in Application of the Guidelines in specic circumstances chapter,this chapter, including including the (Chapter 6) background documents Climate change, Emergencies, Rainwater harvesting, Desalination forfor each cchemical, hemical, is pro-pro- systems, Travellers, Planes and vided in Annex 22.. ships, etc. 12.1 Chemical contaminants in drinking-water Acrylamide Residual acrylamideacrylamide monomermonomer occursoccurs inin polyacrylamidepolyacrylamide coagulantscoagulants used used in in thethe treattreat-- ment of drinking-water. In general, thethe maximummaximum authorizedauthorized dosedose ofof polymerpolymer isis 11 mg/l. mg/l. At a monomer content of 0.05%, this corresponds to a maximum theoretical concen-- trationtration ofof 0.5 µg/l of the monomer in water.water. Practical concentrations maymay bebe lowerlower byby aa factor factor of 2–3. This applies applies to to thethe anionic anionic and and non-ionic non-ionic polyacrylamides, polyacrylamides, but but residual residual levelslevels fromfrom cationic polyacrylamides maymay bebe higher.higher.
    [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]
  • Mecoprop Final V3.1
    Science Group report NC/03/12 Attenuation of mecoprop in the subsurface Environment Agency Science Group: Air, Land & Water The Environment Agency is the leading public body protecting and improving the environment in England and Wales. It’s our job to make sure that air, land and water are looked after by everyone in today’s society, so that tomorrow’s generations inherit a cleaner, healthier world. Our work includes tackling flooding and pollution incidents, reducing industry’s impacts on the environment, cleaning up rivers, coastal waters and contaminated land, and improving wildlife habitats. Authors: Published by: J. Thrasher1, P. Morgan2 & S. R. Buss2. 1 Jacobs Gibb, Gibb House, London Road, Reading, RG6 1BL. Environment Agency 2 Rio House Environmental Simulations International Ltd, Priory House, Priory Road, Shrewsbury, SY1 1RU. Waterside Drive, Aztec West Almondsbury, Bristol, BS32 4UD Statement of use: Tel: 01454 624400 Fax: 01454 624409 This report presents a literature review of mecoprop attenuation processes in the subsurface environment. It IC Code: BHST includes summarised rates for biodegradation and sorption reactions from field and laboratory experiments. The © Environment Agency, March 2004 presented data may be used for initial risk-screening, but site-specific data collection is expected where the output All rights reserved. This document may be reproduced with from an initial assessment of pollution risks is indicates that prior permission of the Environment Agency. it is sensitive to mecoprop attenuation parameters. This report is printed on Cyclus Print, a 100% recycled stock, which is 100% post consumer waste and is totally chlorine free. Environment Agency project manager: Water used is treated and in most cases returned to source in Jonathan Smith, Science Group: Air, Land & Water better condition than removed.
    [Show full text]
  • 2019 Minnesota Chemicals of High Concern List
    Minnesota Department of Health, Chemicals of High Concern List, 2019 Persistent, Bioaccumulative, Toxic (PBT) or very Persistent, very High Production CAS Bioaccumulative Use Example(s) and/or Volume (HPV) Number Chemical Name Health Endpoint(s) (vPvB) Source(s) Chemical Class Chemical1 Maine (CA Prop 65; IARC; IRIS; NTP Wood and textiles finishes, Cancer, Respiratory 11th ROC); WA Appen1; WA CHCC; disinfection, tissue 50-00-0 Formaldehyde x system, Eye irritant Minnesota HRV; Minnesota RAA preservative Gastrointestinal Minnesota HRL Contaminant 50-00-0 Formaldehyde (in water) system EU Category 1 Endocrine disruptor pesticide 50-29-3 DDT, technical, p,p'DDT Endocrine system Maine (CA Prop 65; IARC; IRIS; NTP PAH (chem-class) 11th ROC; OSPAR Chemicals of Concern; EuC Endocrine Disruptor Cancer, Endocrine Priority List; EPA Final PBT Rule for 50-32-8 Benzo(a)pyrene x x system TRI; EPA Priority PBT); Oregon P3 List; WA Appen1; Minnesota HRV WA Appen1; Minnesota HRL Dyes and diaminophenol mfg, wood preservation, 51-28-5 2,4-Dinitrophenol Eyes pesticide, pharmaceutical Maine (CA Prop 65; IARC; NTP 11th Preparation of amino resins, 51-79-6 Urethane (Ethyl carbamate) Cancer, Development ROC); WA Appen1 solubilizer, chemical intermediate Maine (CA Prop 65; IARC; IRIS; NTP Research; PAH (chem-class) 11th ROC; EPA Final PBT Rule for 53-70-3 Dibenzo(a,h)anthracene Cancer x TRI; WA PBT List; OSPAR Chemicals of Concern); WA Appen1; Oregon P3 List Maine (CA Prop 65; NTP 11th ROC); Research 53-96-3 2-Acetylaminofluorene Cancer WA Appen1 Maine (CA Prop 65; IARC; IRIS; NTP Lubricant, antioxidant, 55-18-5 N-Nitrosodiethylamine Cancer 11th ROC); WA Appen1 plastics stabilizer Maine (CA Prop 65; IRIS; NTP 11th Pesticide (EPA reg.
    [Show full text]
  • INSECT, WEED, Anddisease CONTROL in TURFGRASS
    SC-039 5/17 WEED,INSECT, and DISEASE CONTROL in TURFGRASS 2017–18 WEED, INSECT, and DISEASE CONTROL in TURFGRASS Editor Casey Reynolds, Assistant Professor and Extension Turfgrass Specialist Authors Casey Reynolds, Assistant Professor and Extension Turfgrass Specialist Matt Elmore, Assistant Professor and Extension Turfgrass Specialist Young-Ki Jo, Associate Professor and Extension Turfgrass Specialist Diane Silcox Reynolds, Post-doctoral Research Associate, Entomology AggieTurf: http://aggieturf.tamu.edu Contents Introduction . 1 Herbicide Mode of Action (MOA) classification . 3 Herbicides for general control of grassy and broadleaf weeds . 4 Preemergence herbicides for grassy and broadleaf weeds . 4 Selective postemergence herbicides . 9 Synthetic auxin postemergence herbicides for broadleaf weeds . 19 Product formulations containing synthetic auxin herbicides . 21 Nonsynthetic auxin postemergence herbicides for broadleaf weeds . 23 Nonselective herbicides for general weed control . 24 Herbicides for commonly occurring weeds . 25 Crabgrass (Digitaria spp ). 25 Goosegrass (Eleusine indica) . 27 Sandbur (Cenchrus spp ). 30 Annual bluegrass (Poa annua L ). 33 Dallisgrass (Paspalum dilatatum Poir ). 39 WEEDS Bermudagrass (Cynodon spp ). 41 Nutsedge (Cyperus spp ). and kyllinga (Kyllinga spp ). 43 Khakiweed and mat chafflower (Alternanthera spp ). 46 Herbicides containing sulfentrazone . 47 Herbicides containing quinclorac . 48 Turfgrass tolerance to postemergence herbicides . 49 Plant growth regulators . 51 Insect pests in turfgrasses . 53 Insecticide Mode of Action (MOA) classification . 55 Insecticides registered for use in turfgrasses . 56 Ants . 56 Armyworms . 58 Billbugs . 61 Black turfgrass ataenius . 63 Chinch bugs . 66 Cutworms . 69 Green June beetles . 72 Mealybugs . 74 Mites . 75 INSECTS Mole crickets . 76 Red imported fire ants . 79 Sod webworms . 81 White grubs . 84 Diseases in Texas turfgrasses . 86 Fungicide Mode of Action (MOA) classification .
    [Show full text]