University Microfilms, Inc., Ann Arbor, Michigan the MOVEMENT and PERSISTENCE of SIMAZINE and ATRAZINE in SOIL

Total Page:16

File Type:pdf, Size:1020Kb

University Microfilms, Inc., Ann Arbor, Michigan the MOVEMENT and PERSISTENCE of SIMAZINE and ATRAZINE in SOIL This dissertation has been 62—817 microfilmed exactly as received STROUBE, Edward White, 1927- THE MOVEMENT AND PERSISTENCE OF SIMAZINE AND ATRAZENE IN SOIL AND SOME RELATED STUDIES. The Ohio State University, Ph.D., 1961 Agriculture, plant culture University Microfilms, Inc., Ann Arbor, Michigan THE MOVEMENT AND PERSISTENCE OF SIMAZINE AND ATRAZINE IN SOIL AND SOME RELATED STUDIES DISSERTATION Presented in Partial Fulfillment of the Requirements for the Degree Doctor of Philosophy in the Graduate School of The Ohio State University By Edward White Stroube, B.S., M.S. -i « The Ohio State University 1961 Approved by Department of Agronomy ACKNOWLEDGMENTS The author gratefully appreciates the guidance and direction given by Drs. D. D. Bondarenko and C. J. Willard in the course of this study. Sincere appreciation is also extended to Drs. S. R. Anderson, E. K. Alban, D. A. Ray and P. E. Smith for their helpful suggestions and constructive criticisms during the preparation of this manuscript. The author wishes to thank the faculty and staff members and fellow graduate students of the Department of Agronomy for their inter­ est and assistance during the course of this study. Gratitude is expressed to the Geigy Chemical Corporation for some of the materials used in this investigation. The author is deeply grateful to his wife for the encouragement, assistance and sacrifices made by her during this study. ii CONTENTS Page INTRODUCTION ...................... 1 REVIEW OF LITERATURE ................................. 3 The effectiveness of simazine as an herbicide when applied to corn.............................................................. 3 The movement and persistence of herbicides in so i l s ........... 8 The effect of herbicides on soil microorganisms................ 18 EXPERIMENTAL MATERIALS AND METHODS ...................... 22 Properties and source of herbicides ...................... 22 ? The effect of simazine on weed population and corn yield. 23 The effect of simazine soil residues on corn, wheat, barley, oats and soybeans ............................ 25 The movement of simazine in soil in the fie l d ................... 28 The movement of simazine and atrazine in soil in the laboratory. ............... 29 The effect of soil microorganisms on the breakdown of simazine and the effect of simazine on the activity of soil micro­ organisms ........................................................ 33 EXPERIMENTAL RESULTS AND DISCUSSION................................. 36 The effect of simazine on weed population and corn yield. 36 The effect of simazine soil residues on com, wheat, barley, oats and soybeans ............................................... 37 The movement of simazine in soil in the fi e l d ................... 45 The movement of simazine and atrazine in soil in the laboratory...................... 57 iii CONTENTS Page The effect of soil microorganisms on the breakdown of simazine . 61 The effect of simazine on the activity of soil microorganisms. 66 SUMMARY AND CONCLUSIONS ..............................................70 LITERATURE CITED.......................................................73 APPENDIX................................................................81 AUTOBIOGRAPHY .......................................................... 88 iv LIST OF TABLES Table Page 1. Number and per cent reduction of annual broadleaf and grass weeds in corn treated pre-emergence with simazine on May 25, 1959. Counts were made on June 20, 1959, on 175 sq. ft. of each of 4 replicates. Values are the average of 4 replications........................ 36 2. Yield of corn treated pre-emergence with simazine on May 25, 1959. Average of 4 replications ....................... 37 3. Yield of corn, wheat, barley, oats and soybeans following corn treated pre-emergence with simazine. Values shown are the averages of four replications. ..................38 4. Rainfall at University Farm, Columbus, O h i o ................... 38 5. Weight of first crop of oat seedlings grown in soil taken on October 15, 1959, from field plots treated with simazine on May 25, 1959. Values are grams of fresh weight and are the average of three replications .... 46 6. Weight of second crop of oat seedlings grown in soil taken on October 15, 1959, from field plots treated with simazine on May 25, 1959. Values are grams of fresh weight and are the average of three replications. 47 7. Bioassay standards for weight of oat seedlings grown in soil freshly treated with simazine and randomized with soil taken from field plots on October 15, 1959. Values are grams of fresh weight and are the average of three replications ........................................... 47 8. Weight of first crop of oat seedlings grown in soil taken on May 12, 1960, from field plots treated with simazine on May 25, 1959. Values are grams of fresh weight and are the average of three replications...................... 51 9. Weight of second crop of oat seedlings grown in soil taken on May 12, 1960, from field plots treated with simazine on May 25, 1959. Values are grams of fresh weight and are the average of three replications.......... 52 v LIST OF TABLES Table Page 10. Bioassay standards for weight of oat seedlings grown in soil freshly treated with simazine and randomized with soil taken from field plots on May 12, 1960. Values are grams of fresh weight and are the average of three replications ............................................... 54 11. Weight of first crop of oat seedlings grown in soil taken on October 10, 1960, from field plots treated with simazine on May 25, 1959. Values are grams of fresh weight and are the average of three replications .... 54 12. Weight of second crop of oat seedlings grown in soil taken on October 10, 1960, from field plots treated with simazine on May 25, 1959. Values are grams of fresh weight and are the average of three replications .... 55 13. Bioassay standards for weight of oat seedlings grown in soil freshly treated with simazine and randomized with soil taken from field plots on October 10, 1960. Values are grams of fresh weight and are the average of three replications ........................................... 55 14. Weight of oat seedlings grown in two soil types treated with atrazine and simazine. Water was applied to the treated soil surfaces and the soil columns were sectioned into five one-inch levels. Values are grams fresh weight and are the average of three replications..................... 58 15. Weight of oat seedlings grown in two soil types treated with atrazine and simazine. Four rates of water were applied to the treated soil surfaces. Values are grams fresh weight and are the average of three replications .... 59 16. Weight of oat seedlings grown in soil treated with atra­ zine and simazine. Four rates of water were applied to the treated soil surfaces and the soil columns were sectioned into five one-inch levels. Values are grams fresh weight and are the average of three replications . 62 17. Amount of carbon, evolved as carbon dioxide, from 100 grams of non-treated and simazine treated soil. Values are grams of carbon and are the average of four replications ............................................ 69 18. Analysis of variance for yield of corn treated pre­ emergence with simazine on May 25, 1959................... 81 19. Analysis of variance for yields of com, wheat, barley, oats and soybeans.......................................... 82 vi LIST OF TABLES Table Page 20. Analysis of variance for weight of first crop of oats grown in simazine treated soil taken from field plots on October 15, 1959.......................................... 83 21. Analysis of variance for weight of second crop of oats grown in simazine treated soil taken from field plots on October 15, 1959.......................................... 83 22. Analysis of variance for weight of first crop of oats grown in simazine treated soil taken from field plots on May 12, 1960......................................... 84 23. Analysis of variance for weight of second crop of oats grown in simazine treated soil taken from field plots on May 12, 1960....................................... 84 24. Analysis of variance for weight of first crop of oats grown in simazine treated soil taken from field plots on October 10, 1960........................... 85 25. Analysis of variance for weight of second crop of oats grown in simazine treated soil taken from field plots on October 10, 1960.......................................... 85 26. Analysis of variance for weight of oat seedlings grown on soil treated with atrazine and simazine which were leached with varying amounts of water applied to the soil surface ..................................................86 27. Analysis of variance for the amount of carbon, evolved as carbon dioxide, from 100 grams of non-treated and sima­ zine treated soil............................................. 87 vii LIST OF FIGURES Figure Page 1. Field plot design of experiment to determine the effects of simazine residue in soil on corn, wheat, barley, oats and soybeans. Simazine was applied at 0, 2, 4 and 8 pounds per acre on May 25, 1959, and the crops were planted on the indicated dates......................... 26 2. The yield of com, wheat, barley, oats and soybeans following c o m treated pre-emergence with simazine. Yield expressed as per cent of c h e c k ....................... 39 3. The growth of c o m in 1960 in plots receiving (left) no simazine and (right) 8 pounds of simazine per acre. The simazine was applied in May 1959
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]
  • 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.
    [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]
  • 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]
  • 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.
    [Show full text]
  • 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
    [Show full text]
  • 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,
    [Show full text]
  • 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.
    [Show full text]
  • Turfgrass Weed Control
    MP521 Turfgrass Weed Control DIVISION OF AGRICULTURE R E S E A R C H & E X T E N S I O N University of Arkansas, United States Department of Agriculture, University of Arkansas System and County Governments Cooperating Contents Introduction to Turfgrass Weed Control .............. 3 Hairy Bittercress ................................................... 11 American Burnweed ............................................. 4 Henbit .................................................................. 11 Annual Bluegrass .................................................. 4 Kyllinga................................................................. 12 Annual Sedge........................................................ 4 Large Hop Clover................................................. 12 Bahiagrass ............................................................. 5 Lawn Burweed or Spurweed ................................ 12 Bermudagrass – Preplant Control ......................... 5 Lespedeza, Common ............................................ 13 Bermudagrass – Selective Suppression.................. 5 Lyreleaf Sage......................................................... 13 Carolina Geranium ............................................... 6 Moss ..................................................................... 13 Carpetweed ........................................................... 6 Nutsedge, Purple................................................... 14 Cat’s Ear Dandelion ............................................. 6 Nutsedge, Yellow..................................................
    [Show full text]
  • Volatilization of Alachlor and Atrazine As Influenced by Surface Litter" (1995)
    University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln U.S. Department of Agriculture: Agricultural Publications from USDA-ARS / UNL Faculty Research Service, Lincoln, Nebraska 1995 Volatilization of Alachlor and Atrazine as Influenced yb Surface Litter Timothy Gish USDA-ARS Ali Sadeghi USDA-ARS Brian J. Wienhold University of Nebraska-Lincoln, [email protected] Follow this and additional works at: https://digitalcommons.unl.edu/usdaarsfacpub Gish, Timothy; Sadeghi, Ali; and Wienhold, Brian J., "Volatilization of Alachlor and Atrazine as Influenced by Surface Litter" (1995). Publications from USDA-ARS / UNL Faculty. 1191. https://digitalcommons.unl.edu/usdaarsfacpub/1191 This Article is brought to you for free and open access by the U.S. Department of Agriculture: Agricultural Research Service, Lincoln, Nebraska at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Publications from USDA-ARS / UNL Faculty by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Chemosphere, Vol. 31, No. 4, pp. 2971-2982, 1995 ~n Elsevier Scielice Ltd 0045-6535(95)00157-3 Printed in Great Britain Vdalilimflo. of Aladflor and ~ as l~em:~! by Surface Litter Timothy J. Gish*, All Sadeghi*', and Brian J. Wienhold"" * Soil Physicist, Hydrology Laboratory, Natural Resources Institute, U. S. Department of Agriculture, Agricultural Research Service, Beltsville, Maryland 20705, USA. " Soil Scientist, Environmental Chemistry Laboratory, Natural Resources Institute, U. S. Department of Agriculture, Agricultural Research Service, Bcitsville, Maryland 20705, USA. "'" Soil Scientist, Northern Great Plains Research Laboratory, U. S. Department of Agriculture, Agricultural Research Service, Mandan, North Dakota 58554, USA (Received in Germany 4 April 1995; accepted 1 June 1995) ABSTRACT A basic knowledge of how herbicide volatilization is influenced by agronomic practices is necessary if long-term detrimental impacts from herbicides are to be minimized.
    [Show full text]
  • Herbicides in Pooled Raw Milk in Connecticut
    136 Journal of Food Protection, Vol. 54, No. 2, Pages 136-137 (February 1991) Copyright© International Association of Milk, Food and Environmental Sanitarians Herbicides in Pooled Raw Milk in Connecticut HARRY M. PYLYPIW, JR. and LESTER HANKIN* Department of Analytical Chemistry, The Connecticut Agricultural Experiment Station, Box 1106, New Haven, Connecticut 06504 Downloaded from http://meridian.allenpress.com/jfp/article-pdf/54/2/136/1662776/0362-028x-54_2_136.pdf by guest on 29 September 2021 (Received for publication June 29, 1990) ABSTRACT and Drug Administration) (2). Concentrations found of these pesticides were always well below the action level. Pooled raw milk samples collected in Connecticut were Since cows in Connecticut consume quantities of corn analyzed for the herbicides 2,4-D, Atrazine, Simazine, and Alachlor. silage and grass, we investigated milk for the presence of For 2,4-D, 25.6% of the samples had no detectable level, for herbicides used on these feeds. Atrazine 7.7%, and for Alachlor 10.3%. None contained Simaz­ ine. Concentrations averaged 0.021 ppm for 2,4-D, 0.0075 for MATERIALS AND METHODS Atrazine, and 0.0067 for Alachlor. No sample exceeded the EPA tolerance for any of the herbicides. Analysis was by enzyme immunoassay. A total of 78 samples was collected in Connecticut from milk tank trucks from January to April, 1990 by inspectors of the Dairy Division of the Connecticut Department of Agricul­ ture. Each sample was from a pooled supply from the tank truck Field corn is a major agricultural crop in Connecticut. and represented from 1 to 7 farms.
    [Show full text]
  • California Turfgrass Culture
    California Turfgrass Culture FORMERLY, SOUTHERN CALIFORNIA TURFGRASS CULTURE OCTOBER 1963 VOLUME 13 - NUMBER 4 Regulation of Sodium Arsenite as an Injurious Material John C. Hillis California Department of Agriculture Sacramento Effective January 1, 1962, sodium arsenite was placed pest or vegetation which it is intended to destroy. Thus under regulation as an injurious material. Since then, an injurious material sold for weed control or control of a persons intending to use it in California have been re- plant disease or of a micro-organism is subject to the quired to obtain a permit from the county agricultural requirement of a permit. On the other hand, if sodium commissioner. In addition, it is illegal to sell or deliver arsenite is sold for a non-agricultural and non-pesticidal it to persons who do not have the required permit. use, for example, in metallurgy, or in drilling to facilitate the operation mechanically, the use would not be subject The regulation was adopted after public hearing and to the requirement of a permit. consideration of the history of accidental deaths over the years as well as injury to property. All sizes of sodium arsenite pesticide containers are subject to the requirement of a permit; however, there is Section 1080 of the Agricultural Code provides that an exemption in that no permit is required to use products “after investigation and hearing the Director shall adopt sold as dilute ready-to-use syrups or dry baits, registered rules and regulations governing the application, in pest and labeled for use as poison baits for the control of control or other agricultural operations, of any material he insects and other arthropods, snails and slugs, or rodents.
    [Show full text]