PERSISTENT ORGANIC POLLUTANTS DDT-Aldrin
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Restricted Use Product Summary Report
Page 1 of 17 Restricted Use Product Summary Report (January 19, 2016) Percent Active Registration # Name Company # Company Name Active Ingredient(s) Ingredient 4‐152 BONIDE ORCHARD MOUSE BAIT 4 BONIDE PRODUCTS, INC. 2 Zinc phosphide (Zn3P2) 70‐223 RIGO EXOTHERM TERMIL 70 VALUE GARDENS SUPPLY, LLC 20 Chlorothalonil 100‐497 AATREX 4L HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 42.6 Atrazine 100‐585 AATREX NINE‐O HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 88.2 Atrazine 100‐669 CURACRON 8E INSECTICIDE‐MITICIDE 100 SYNGENTA CROP PROTECTION, LLC 73 Profenofos 100‐817 BICEP II MAGNUM HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 33; 26.1 Atrazine; S‐Metolachlor 100‐827 BICEP LITE II MAGNUM HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 28.1; 35.8 Atrazine; S‐Metolachlor 100‐886 BICEP MAGNUM 100 SYNGENTA CROP PROTECTION, LLC 33.7; 26.1 Atrazine; S‐Metolachlor 100‐898 AGRI‐MEK 0.15 EC MITICIDE/INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 2 Abamectin 100‐903 DENIM INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 2.15 Emamectin benzoate 100‐904 PROCLAIM INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 5 Emamectin benzoate 100‐998 KARATE 1EC 100 SYNGENTA CROP PROTECTION, LLC 13.1 lambda‐Cyhalothrin 100‐1075 FORCE 3G INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 3 Tefluthrin Acetochlor; Carbamothioic acid, dipropyl‐ 100‐1083 DOUBLEPLAY SELECTIVE HERBICIDE 100 SYNGENTA CROP PROTECTION, LLC 16.9; 67.8 , S‐ethyl ester 100‐1086 KARATE EC‐W INSECTICIDE 100 SYNGENTA CROP PROTECTION, LLC 13.1 lambda‐Cyhalothrin 100‐1088 SCIMITAR GC INSECTICIDE 100 SYNGENTA CROP PROTECTION, -
Cypermethrin
International Environmental Health Criteria 82 Cypermethrin Published under the joint sponsorship of the United Nations Environment Programme, the International Labour Organisation, and the World Health Organization WORLD HEALTH ORGANIZATION GENEVA 1989 Other titles available in the ENVIRONMENTAL HEALTH CRITERIA series include: 1. Mercury 2. Polychlorinated Biphenyls and Terphenyls 3. Lead 4. Oxides of Nitrogen 5. Nitrates, Nitrites, and N-Nitroso Compounds 6. Principles and Methods for Evaluating the Toxicity of Chemicals, Part 1 7. Photochemical Oxidants 8. Sulfur Oxides and Suspended Particulate Matter 9. DDT and its Derivatives 10. Carbon Disulfide 11. Mycotoxins 12. Noise 13. Carbon Monoxide 14. Ultraviolet Radiation 15. Tin and Organotin Compounds 16. Radiofrequency and Microwaves 17. Manganese 18. Arsenic 19. Hydrogen Sulfide 20. Selected Petroleum Products 21. Chlorine and Hydrogen Chloride 22. Ultrasound 23. Lasers and Optical Radiation 24. Titanium 25. Selected Radionuclides 26. Styrene 27. Guidelines on Studies in Environmental Epidemiology 28. Acrylonitrile 29. 2,4-Dichlorophenoxyacetic Acid (2,4-D) 30. Principles for Evaluating Health Risks to Progeny Associated with Exposure to Chemicals during Pregnancy 31. Tetrachloroethylene 32. Methylene Chloride 33. Epichlorohydrin 34. Chlordane 35. Extremely Low Frequency (ELF) Fields 36. Fluorine and Fluorides 37. Aquatic (Marine and Freshwater) Biotoxins 38. Heptachlor 39. Paraquat and Diquat 40. Endosulfan 41. Quintozene 42. Tecnazene 43. Chlordecone 44. Mirex continued on p. 156 -
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Guidelines for Interpretation of the Biological Effects of Selected Constituents in Biota, Water, and Sediment November 1998 NIATIONAL RRIGATION WQATER UALITY P ROGRAM INFORMATION REPORT No. 3 United States Department of the Interior Bureau of Reclamation Fish and Wildlife Service Geological Survey Bureau of Indian Affairs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ntroduction The guidelines, criteria, and other information in The Limitations of This Volume this volume were originally compiled for use by personnel conducting studies for the It is important to note five limitations on the Department of the Interior's National Irrigation material presented here: Water Quality Program (NIWQP). The purpose of these studies is to identify and address (1) Out of the hundreds of substances known irrigation-induced water quality and to affect wetlands and water bodies, this contamination problems associated with any of volume focuses on only nine constituents or the Department's water projects in the Western properties commonly identified during States. When NIWQP scientists submit NIWQP studies in the Western United samples of water, soil, sediment, eggs, or animal States—salinity, DDT, and the trace tissue for chemical analysis, they face a elements arsenic, boron, copper, mercury, challenge in determining the sig-nificance of the molybdenum, selenium, and zinc. -
Carpenter Ants and Control in Homes Page 1 of 6
Carpenter Ants and Control in Homes Page 1 of 6 Carpenter Ants and Control in Homes Fact Sheet No. 31 Revised May 2000 Dr. Jay B Karren, Extension Entomologist Alan H. Roe, Insect Diagnostician Introduction Carpenter ants are members of the insect order Hymenoptera, which includes bees, wasps, sawflies, and other ants. Carpenter ants can be occasional pests in the home and are noted particularly for the damage they can cause when nesting in wood. In Utah they are more of a nuisance rather than a major structural pest. Carpenter ants, along with a number of other ant species, utilize cavities in wood, particularly stumps and logs in decayed condition, as nesting sites. They are most abundant in forests and can be easily found under loose bark of dead trees, stumps, or fallen logs. Homeowners may bring them into their homes when they transport infested logs from forests to use as firewood. Description Carpenter ants include species that are among the largest ants found in the United States. They are social insects with a complex and well-defined caste system. The worker ants are sterile females and may occur in different sizes (majors and minors). Members of the reproductive caste (fertile males and females) are usually winged prior to mating. All ants develop from eggs deposited by a fertilized female (queen). The eggs hatch into grub-like larvae (immatures) which are fed and cared for by the workers. When fully grown, the larvae spin a cocoon and enter the pupal stage. The pupal stage is a period of transformation from the larva to adult. -
3R Toolkit for the MICE Industry
for the Meetings, Incentives, 3R Conventions & Toolkit Exhibitions Industry Supported by: CONTENTS 03 Introduction 04 Recommended 3R Practices Case Study on Singapore 09 International Building Week Case Study on Oracle 14 OpenWorld 19 Who to Contact ACKNOWLEDGEMENTS The MICE 3R Toolkit is an initiative of the MICE 3R taskforce comprising the National Environment Agency (NEA), the Singapore Tourism Board (STB) and members of the Singapore Association of Conference and Exhibition Organisers and Suppliers (SACEOS) to provide guidance on 3R initiatives for the MICE industry. A note of thanks to the following taskforce members for their invaluable contributions and support in producing this toolkit: Globibo Singapore Dr Felix Rimbach, Director of Research & Development Marina Bay Sands Pte Ltd Mr Kevin Teng, Executive Director of Sustainability Mr Roger Simons, Associate Director of Sustainability Reed Exhibitions Singapore Ms Louise Chua, Project Director of the Building & Energy Cluster Singapore Tourism Board Ms Keeva Lim, Lead Specialist of Conventions, Meetings & Incentive Travel Suntec Singapore Convention & Exhibition Centre Mr Daniel Ang, Senior Director of Operations Waste Management and Recycling Association of Singapore Mr Michael Ho, Vice Chairman Our thanks also go to Mr Paul Salinger, Vice President of Marketing of Oracle, and Ms Cressida Slote, Sustainability Project Manager of MeetGreen, for their assistance with the case study on Oracle OpenWorld. MICE 3R Toolkit 02 7.8 million tonnes of waste was generated in Singapore in 2016. If waste output continues to grow, more incineration plants will have to be built and Semakau Landfill will run out of space by 2035 or earlier. Resources such as water and energy are conserved when we reduce, reuse and recycle. -
Draft Scope of the Risk Evaluation for Triphenyl Phosphate CASRN 115-86-6
EPA Document# EPA-740-D-20-010 April 2020 United States Office of Chemical Safety and Environmental Protection Agency Pollution Prevention Draft Scope of the Risk Evaluation for Triphenyl Phosphate CASRN 115-86-6 April 2020 TABLE OF CONTENTS ACKNOWLEDGEMENTS ......................................................................................................................5 ABBREVIATIONS AND ACRONYMS ..................................................................................................6 EXECUTIVE SUMMARY .......................................................................................................................8 1 INTRODUCTION ............................................................................................................................11 2 SCOPE OF THE EVALUATION ...................................................................................................11 2.1 Reasonably Available Information ..............................................................................................11 Search of Gray Literature ...................................................................................................... 12 Search of Literature from Publicly Available Databases (Peer-Reviewed Literature) .......... 13 Search of TSCA Submissions ................................................................................................ 19 2.2 Conditions of Use ........................................................................................................................19 Categories -
A COMPARATIVE STUDY of the CYTOGENETIC EFFECTS of the INSECTICIDES HEPTACHLOR, MALATHION, and METHYL PARATHION in Vicia Faba
Contam. Amb. 1, 7-16, 1985 A COMPARATIVE STUDY OF THE CYTOGENETIC EFFECTS OF THE INSECTICIDES HEPTACHLOR, MALATHION, AND METHYL PARATHION IN Vicia faba SANDRAGOMEZ-ARROYO, ANA MAR~ABAIZA, GRA~IELALOPEZ AND RAFAELVILLALOBOS- PIETRINI Laboratorio de Citogenética y Mutagénesis Am- bientales, Centro de Ciencias de la Atmósfera, Universidad Nacional Autónoma de México, Co- yoacán 04510, México, D. F. y Centro de Inves- tigación y Reproducción Animal, Universidad Au- tónoma de Tlaxcala. ABSTRACT In order to determine the potential cytogenetic effects of Heptachlor, Malathion and Methyl Parathion, meristems of broad bean root tips were treated with se- vera1 concentrations o£ these insecticides for different periods of treatment and recovery. Heptachlor and Malathion induced chromosomal alterations in anaphase cells as fragments and bridges, chromosomes with inactivated centromeres and isochroinosomes, and as micronuclei in interphase cells. Multipolar anaphases also appeared when the mitotic spindle was damaged. Heptachlor induced pycnosis but Malathion did not. Chromosomal aberrations caused by Methyl Parathion were observed in cells only during metaphase, since a strong c-mitotic effect was induced mostly in the form of fragments. Longer recovery periods (42 and 44 h) revealed tetraploid and pycnotic cells. Only in the case of Malation was there an increase in chromosome altera- tions with higher concentrations. However, no such dose response relationship was observed for micronuclei frequency. RESUMEN Con el fin de establecer el daño genético que ocasionan el Heptacloro, el Mala- tión y el Metil Paratión, se realizaron tratamientos sobre las células meristemá- ticas de la raíz de haba con diversas concentraciones de estos insecticidas y dife- rentes tiempos de tratamiento y recuperación. -
Appendix H EPA Hazardous Waste Law
Appendix H EPA Hazardous Waste Law This Appendix is intended to give you background information on hazardous waste laws and how they apply to you. For most U.S. Environmental Protection Agency (EPA) requirements that apply to the University, the Safety Department maintains compliance through internal inspections, record keeping and proper disposal. In Wisconsin, the Department of Natural Resources (DNR) has adopted the EPA regulations, consequently EPA and DNR regulations are nearly identical. EPA defines This Appendix only deals with "hazardous waste" as defined by the EPA. hazardous waste as Legally, EPA defines hazardous waste as certain hazardous chemical waste. This hazardous chemical Appendix does not address other types of regulated laboratory wastes, such as waste; radioactive, infectious, biological, radioactive or sharps. Chapter 8 descibes disposal procedures infectious and biohazardous waste for animals. Chapter 9 describes disposal procedures for sharps and other waste that are regulated by can puncture tissue. Chapter 11 discusses Radiation and the Radiation Safety for other agencies. Radiation Workers provides guidelines for the disposal of radioactive waste. Procedures for medical waste are written by the UW Hospital Safety Officer. The Office of Biological Safety can provide guidance for the disposal of infectious and biological waste. EPA regulations focus on industrial waste streams. As a result, many laboratory chemical wastes are not regulated by EPA as hazardous chemical waste. However, many unregulated chemical wastes do merit special handling and disposal If a waste can be procedures. Thus, Chapter 7 and Appendix A of this Guide recommend disposal defined as: procedures for many unregulated wastes as if they were EPA hazardous waste. -
Historical Use of Lead Arsenate and Survey of Soil Residues in Former Apple Orchards in Virginia
HISTORICAL USE OF LEAD ARSENATE AND SURVEY OF SOIL RESIDUES IN FORMER APPLE ORCHARDS IN VIRGINIA by Therese Nowak Schooley Thesis submitted to the faculty of the Virginia Polytechnic Institute and State University in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE IN LIFE SCIENCES in Entomology Michael J. Weaver, Chair Donald E. Mullins, Co-Chair Matthew J. Eick May 4, 2006 Blacksburg, Virginia Keywords: arsenic, lead, lead arsenate, orchards, soil residues, historical pesticides HISTORICAL USE OF LEAD ARSENATE AND SURVEY OF SOIL RESIDUES IN FORMER APPLE ORCHARDS IN VIRGINIA Therese Nowak Schooley Abstract Inorganic pesticides including natural chemicals such as arsenic, copper, lead, and sulfur have been used extensively to control pests in agriculture. Lead arsenate (PbHAsO4) was first used in apple orchards in the late 1890’s to combat the codling moth, Cydia pomonella (Linnaeus). The affordable and persistent pesticide was applied in ever increasing amounts for the next half century. The persistence in the environment in addition to the heavy applications during the early 1900’s may have led to many of the current and former orchards in this country being contaminated. In this study, soil samples were taken from several apple orchards across the state, ranging from Southwest to Northern Virginia and were analyzed for arsenic and lead. Based on naturally occurring background levels and standards set by other states, two orchards sampled in this study were found to have very high levels of arsenic and lead in the soil, Snead Farm and Mint Spring Recreational Park. Average arsenic levels at Mint Spring Recreational Park and Snead Farm were found to be 65.2 ppm and 107.6 ppm, respectively. -
TOXICOLOGICAL PROFILE for HEPTACHLOR and HEPTACHLOR EPOXIDE
TOXICOLOGICAL PROFILE FOR HEPTACHLOR and HEPTACHLOR EPOXIDE Prepared by: Syracuse Research Corporation Under Contract No. 200-2004-09793 Prepared for: U.S. DEPARTMENT OF HEALTH AND HUMAN SERVICES Public Health Service Agency for Toxic Substances and Disease Registry November 2007 HEPTACHLOR AND HEPTACHLOR EPOXIDE ii DISCLAIMER The use of company or product name(s) is for identification only and does not imply endorsement by the Agency for Toxic Substances and Disease Registry. HEPTACHLOR AND HEPTACHLOR EPOXIDE iii UPDATE STATEMENT A Toxicological Profile for Heptachlor/Heptachlor Epoxide, Draft for Public Comment was released in September 2005. This edition supersedes any previously released draft or final profile. Toxicological profiles are revised and republished as necessary. For information regarding the update status of previously released profiles, contact ATSDR at: Agency for Toxic Substances and Disease Registry Division of Toxicology and Environmental Medicine/Applied Toxicology Branch 1600 Clifton Road NE Mailstop F-32 Atlanta, Georgia 30333 HEPTACHLOR AND HEPTACHLOR EPOXIDE iv This page is intentionally blank. v FOREWORD This toxicological profile is prepared in accordance with guidelines developed by the Agency for Toxic Substances and Disease Registry (ATSDR) and the Environmental Protection Agency (EPA). The original guidelines were published in the Federal Register on April 17, 1987. Each profile will be revised and republished as necessary. The ATSDR toxicological profile succinctly characterizes the toxicologic and adverse health effects information for the hazardous substance described therein. Each peer-reviewed profile identifies and reviews the key literature that describes a hazardous substance's toxicologic properties. Other pertinent literature is also presented, but is described in less detail than the key studies. -
Mouse Models of Human Disease an Evolutionary Perspective Robert L
170 commentary Evolution, Medicine, and Public Health [2016] pp. 170–176 doi:10.1093/emph/eow014 Mouse models of human disease An evolutionary perspective Robert L. Perlman* Department of Pediatrics, The University of Chicago, 5841 S. Maryland Ave, MC 5058, Chicago, IL 60637, USA *E-mail: [email protected] Received 31 December 2015; revised version accepted 12 April 2016 ABSTRACT The use of mice as model organisms to study human biology is predicated on the genetic and physio- logical similarities between the species. Nonetheless, mice and humans have evolved in and become adapted to different environments and so, despite their phylogenetic relatedness, they have become very different organisms. Mice often respond to experimental interventions in ways that differ strikingly from humans. Mice are invaluable for studying biological processes that have been conserved during the evolution of the rodent and primate lineages and for investigating the developmental mechanisms by which the conserved mammalian genome gives rise to a variety of different species. Mice are less reliable as models of human disease, however, because the networks linking genes to disease are likely to differ between the two species. The use of mice in biomedical research needs to take account of the evolved differences as well as the similarities between mice and humans. KEYWORDS: allometry; cancer; gene networks; life history; model organisms transgenic, knockout, and knockin mice, have If you have cancer and you are a mouse, we can provided added impetus and powerful tools for take good care of you. Judah Folkman [1] mouse research, and have led to a dramatic increase in the use of mice as model organisms. -
Chapter 7.2. Pollution Status of Persistent
LARGE MARINE ECOSYSTEMS: STATUS AND TRENDS Chapter 7.2. Polluton status of persistent organic pollutants Lead Author +LGHVKLJH7DNDGD /DERUDWRU\RI2UJDQLF*HRFKHPLVWU\7RN\R8QLYHUVLW\RI$JULFXOWXUHDQG7HFKQRORJ\ Contributng Author 5HL<DPDVKLWD /DERUDWRU\RI2UJDQLF*HRFKHPLVWU\7RN\R8QLYHUVLW\RI$JULFXOWXUHDQG7HFKQRORJ\ Chapter Citaton 7DNDGD+<DPDVKLWD5 &KDSWHU3ROOXWLRQVWDWXVRISHUVLVWHQWRUJDQLFSROOXWDQWV,Q,2& 81(6&2DQG81(3 Large Marine Ecosystems: Status and Trends8QLWHG1DWLRQV(QYLURQPHQW 3URJUDPPH1DLURELSS 164 POLLUTION AND ECOSYSTEM HEALTH 7.2 Pollution status of persistent organic pollutants SuMMary Persistent organic pollutants (POPs) are man-made chemicals used in industrial and agricultural applicatons; they are widely distributed throughout marine ecosystems. They accumulate in living tssues, become more concentrated through the food chain, and are toxic. POPs pose a health risk to marine biota at higher trophic levels and to human consumers of some sea foods, and have been regulated through the Stockholm Conventon on Persistent Organic Pollutants since 2004. Understanding the status, trends, and distributon of POPs in LMEs, and identfying pollutant sources, are important for assessing and maintaining marine ecosystem health, as well as for evaluatng the efectveness of regulaton. This assessment used plastc resin pellets as passive samplers of POPs in LMEs. The pellets, which are used in the manufacturing of plastc products, are found washed up on beaches all over the world. The pellets sorb and concentrate POPs from the surrounding seawater. Pellets from 193 locatons in 37 LMEs were collected by volunteers through the Internatonal Pellet Watch (IPW) programme between 2005 and 2014 and sent to laboratories to be analysed for three classes of POPs: PCBs (polychlorinated biphenyls), DDTs (dichlorodiphenyltrichloroethane and related chemicals), and HCHs (hexachlorocyclohexane isomers).