NJ Environmental Hazardous Substance List by CAS Number
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Propoxur United States Environmental Protection Agency
United States Prevention, Pesticides EPA738-R-97-009 Environmental Protection And Toxic Substances August 1997 Agency (7508W) Reregistration Eligibility Decision (RED) PROPOXUR UNITED STATES ENVIRONMENTAL PROTECTION AGENCY WASHINGTON, D.C. 20460 OFFICE OF PREVENTION, PESTICIDES AND TOXIC SUBSTANCES CERTIFIED MAIL Dear Registrant: I am pleased to announce that the Environmental Protection Agency has completed its reregistration eligibility review and decisions on the pesticide chemical case propoxur. The enclosed Reregistration Eligibility Decision (RED) contains the Agency's evaluation of the data base of this chemical, its conclusions of the potential human health and environmental risks of the current product uses, and its decisions and conditions under which these uses and products will be eligible for reregistration. The RED includes the data and labeling requirements for products for reregistration. It may also include requirements for additional data (generic) on the active ingredient to confirm the risk assessments. To assist you with a proper response, read the enclosed document entitled "Summary of Instructions for Responding to the RED." This summary also refers to other enclosed documents which include further instructions. You must follow all instructions and submit complete and timely responses. The first set of required responses is due 90 days from the receipt of this letter. The second set of required responses is due 8 months from the date of receipt of this letter. Complete and timely responses will avoid the Agency taking the enforcement action of suspension against your products. If you have questions on the product specific data requirements or wish to meet with the Agency, please contact the Special Review and Reregistration Division representative Bonnie Adler (703) 308-8523. -
ACEPHATE (Addendum)
3 ACEPHATE (addendum) First draft prepared by Professor P.K. Gupta 1 and Dr Angelo Moretto 2 1 Rajinder Nagar, Bareilly, UP, India; 2 Dipartimento Medicina Ambientale e Sanità Pubblica, Università di Padova, Padova, Italy Explanation..........................................................................................................3 Evaluation for acceptable daily intake.................................................................4 Biochemical aspects ......................................................................................4 Oral absorption, distribution, excretion and metabolism .......................4 Toxicological studies.....................................................................................5 Acute toxicity.........................................................................................5 Short-term studies of toxicity.................................................................6 Special studies........................................................................................7 Studies on inhibition of cholinesterase activity in vitro ..................7 Short-term study of neurotoxicity ...................................................7 Developmental neurotoxicity..........................................................9 Observations in humans ..............................................................................10 Comments..........................................................................................................12 Toxicological evaluation ...................................................................................13 -
Common and Chemical Names of Herbicides Approved by the WSSA
Weed Science 2010 58:511–518 Common and Chemical Names of Herbicides Approved by the Weed Science Society of America Below is the complete list of all common and chemical of herbicides as approved by the International Organization names of herbicides approved by the Weed Science Society of for Standardization (ISO). A sponsor may submit a proposal America (WSSA) and updated as of September 1, 2010. for a common name directly to the WSSA Terminology Beginning in 1996, it has been published yearly in the last Committee. issue of Weed Science with Directions for Contributors to A herbicide common name is not synonymous with Weed Science. This list is published in lieu of the selections a commercial formulation of the same herbicide, and in printed previously on the back cover of Weed Science. Only many instances, is not synonymous with the active ingredient common and chemical names included in this complete of a commercial formulation as identified on the product list should be used in WSSA publications. In the absence of label. If the herbicide is a salt or simple ester of a parent a WSSA-approved common name, the industry code number compound, the WSSA common name applies to the parent as compiled by the Chemical Abstracts Service (CAS) with compound only. CAS systematic chemical name or the systematic chemical The chemical name used in this list is that preferred by the name alone may be used. The current approved list is also Chemical Abstracts Service (CAS) according to their system of available at our web site (www.wssa.net). -
Carbamate Pesticides Aldicarb Aldicarb Sulfoxide Aldicarb Sulfone
Connecticut General Statutes Sec 19a-29a requires the Commissioner of Public Health to annually publish a list setting forth all analytes and matrices for which certification for testing is required. Connecticut ELCP Drinking Water Analytes Revised 05/31/2018 Microbiology Total Coliforms Fecal Coliforms/ E. Coli Carbamate Pesticides Legionella Aldicarb Cryptosporidium Aldicarb Sulfoxide Giardia Aldicarb Sulfone Carbaryl Physicals Carbofuran Turbidity 3-Hydroxycarbofuran pH Methomyl Conductivity Oxamyl (Vydate) Minerals Chlorinated Herbicides Alkalinity, as CaCO3 2,4-D Bromide Dalapon Chloride Dicamba Chlorine, free residual Dinoseb Chlorine, total residual Endothall Fluoride Picloram Hardness, Calcium as Pentachlorophenol CaCO3 Hardness, Total as CaCO3 Silica Chlorinated Pesticides/PCB's Sulfate Aldrin Chlordane (Technical) Nutrients Dieldrin Endrin Ammonia Heptachlor Nitrate Heptachlor Epoxide Nitrite Lindane (gamma-BHC) o-Phosphate Metolachlor Total Phosphorus Methoxychlor PCB's (individual aroclors) Note 1 PCB's (as decachlorobiphenyl) Note 1 Demands Toxaphene TOC Nitrogen-Phosphorus Compounds Alachlor Metals Atrazine Aluminum Butachlor Antimony Diquat Arsenic Glyphosate Barium Metribuzin Beryllium Paraquat Boron Propachlor Cadmium Simazine Calcium Chromium Copper SVOC's Iron Benzo(a)pyrene Lead bis-(2-ethylhexyl)phthalate Magnesium bis-(ethylhexyl)adipate Manganese Hexachlorobenzene Mercury Hexachlorocyclopentadiene Molybdenum Nickel Potassium Miscellaneous Organics Selenium Dibromochloropropane (DBCP) Silver Ethylene Dibromide (EDB) -
Determination of the Residual Efficacy of Carbamate and Organophosphate
Yewhalaw et al. Malar J (2017) 16:471 DOI 10.1186/s12936-017-2122-3 Malaria Journal RESEARCH Open Access Determination of the residual efcacy of carbamate and organophosphate insecticides used for indoor residual spraying for malaria control in Ethiopia Delenasaw Yewhalaw1,2†, Meshesha Balkew3†, Josephat Shililu4, Sultan Suleman5, Alemayehu Getachew4, Gedeon Ashenbo4, Sheleme Chibsa6, Gunawardena Dissanayake6, Kristen George7, Dereje Dengela8, Yemane Ye‑Ebiyo4 and Seth R. Irish9* Abstract Background: Indoor residual spraying is one of the key vector control interventions for malaria control in Ethiopia. As malaria transmission is seasonal in most parts of Ethiopia, a single round of spraying can usually provide efective protection against malaria, provided the insecticide remains efective over the entire malaria transmission season. This experiment was designed to evaluate the residual efcacy of bendiocarb, pirimiphos-methyl, and two doses of pro‑ poxur on four diferent wall surfaces (rough mud, smooth mud, dung, and paint). Filter papers afxed to wall surfaces prior to spraying were analyzed to determine the actual concentration applied. Cone bioassays using a susceptible Anopheles arabiensis strain were done monthly to determine the time for which insecticides were efective in killing mosquitoes. Results: The mean insecticide dosage of bendiocarb applied to walls was 486 mg/m2 (target 400/mg). This treat‑ ment lasted 1 month or less on rough mud, smooth mud, and dung, but 4 months on painted surfaces. Pirimiphos- methyl was applied at 1854 mg/m2 (target 1000 mg/m2), and lasted between 4 and 6 months on all wall surfaces. Propoxur with a target dose of 1000 mg/m2 was applied at 320 mg/m2, and lasted 2 months or less on all surfaces, except painted surfaces (4 months). -
3745-100-10 Applicable Chemicals and Chemical Categories
3745-100-10 Applicable chemicals and chemical categories. [Comment: For dates of non-regulatory government publications, publications of recognized organizations and associations, federal rules, and federal statutory provisions referenced in this rule, see the "Incorporation by Reference" section at the end of rule 3745-100-01.] The requirements of this chapter apply to the following chemicals and chemical categories. This rule contains three listings. Paragraph (A) of this rule is an alphabetical order listing of those chemicals that have an associated "Chemical Abstracts Service (CAS)" registry number. Paragraph (B) of this rule contains a CAS registry number order list of the same chemicals listed in paragraph (A) of this rule. Paragraph (C) of this rule contains the chemical categories for which reporting is required. These chemical categories are listed in alphabetical order and do not have CAS registry numbers. (A) Alphabetical listing: -- Chemical Name CAS Number abamectin (avermectin B1) 71751-41-2 acephate (acetylphosphoramidothioic acid o,s-dimethyl ester) 30560-19-1 acetaldehyde 75-07-0 acetamide 60-35-5 acetonitrile 75-05-8 acetophenone 98-86-2 2-acetylaminofluorene 53-96-3 acifluorfen, sodium salt (5- (2-chloro-4- (trifluoromethyl) - phenoxy)-2-nitro-benzoic acid, sodium salt) 62476-59-9 acrolein 107-02-8 acrylamide 79-06-1 acrylic acid 79-10-7 acrylonitrile 107-13-1 alachlor 15972-60-8 aldicarb 116-06-3 aldrin [1,4,5,8-dimethanonaphthalene, 1,2,3,4,10,10-hexachloro- 1,4,4A,5,8,8a-hexahydro- (1 alpha, 4 alpha, 4a beta, 5 -
CAUTION Or Streams with the Product Or Used Containers
PROTECTION OF WILDLIFE, FISH, CRUSTACEANS AND THE ENVIRONMENT Abamectin is extremely toxic to aquatic species. DO NOT contaminate dams, rivers CAUTION or streams with the product or used containers. KEEP OUT OF REACH OF CHILDREN FIRST AID READ SAFETY DIRECTIONS BEFORE OPENING OR USING If poisoning occurs contact a doctor or the Poisons Info Centre. Phone Australia FOR ANIMAL TREATMENT ONLY 13 11 26; New Zealand 0800 764 766. If skin contact occurs, remove contaminated clothing and wash skin thoroughly. ® SAFETY DIRECTIONS EQUITAK EXCEL ORAL PASTE HARMFUL IF SWALLOWED. May irritate the eyes and skin; avoid contact with eyes 3 in 1 Wormer for Horses and skin. Repeated exposure may cause allergic disorders. When opening the container and using the product, wear rubber gloves. Wash hands after use. DESCRIPTION EMERGENCY RESPONSE A pale cream to tan coloured, apple flavoured, palatable paste with a characteristic In case of spillage wear appropriate protective clothing and prevent material from odour and taste. Each gram contains Oxfendazole 200mg, Praziquantel 50mg and entering waterways. Absorb spills with inert material and place in waste containers. Abamectin 4mg. Wash the area with water and absorb with further inert material. Dispose of waste safely. MODE OF ACTION Abamectin stimulates the release of the neurotransmitter GABA in roundworms, MEAT WITHHOLDING PERIOD (HORSES): DO NOT USE less than 28 days which increases the membrane permeability of neurons to chloride ions. Normal before slaughter for human consumption. neural transmission is thus inhibited causing paralysis and death of the parasite. STORAGE Praziquantel affects the attachment of tapeworms to the host tissues by causing Store below 30°C (room temperature), tightly closed, in the original syringe and in spastic paralysis. -
Restricted Use Chemicals by Product Name 09/14/2016
Plant Health - Pesticide and Fertilizer Section 8995 E. Main St. , Reynoldsburg, Ohio 43068 Phone: Phone (614) 728-6396Fax: Fax (614) 728-4221 Governor: John R. Kasich Lt. Governor: Mary Taylor www.agri.ohio.gov [email protected] Director: David T. Daniels Page 1 of 33 Restricted Use Chemicals by Product Name 09/14/2016 Registered Thru: 6/30/2017 12:00:00 AM Product_name Active_Ingredients Company_Name EPA_Number Private Commercial AATREX 4L HERBICIDE INC Atrazine (ANSI) SYNGENTA CROP 100-497 1, 3, 4, 7 2C, 4A, 6A PROTECTION LLC AATREX NINE-O HERBICIDE INC Atrazine (ANSI) SYNGENTA CROP 100-585 1, 3, 4, 7 2C, 4A, 5, 6A, 8 PROTECTION LLC ABACUS AGRICULTURAL MITICIDE/ INSECTICIDE Abamectin ROTAM NORTH 83100-4-83979 3 1, 2A, 2B AMERICA INC ABACUS V Abamectin ROTAM NORTH 83100-32-83979 3 1, 2B, 2C AMERICA INC ABAMECTIN 0.15EC SELECT Abamectin PRIME SOURCE, LLC 89442-20 None None ABAMEX MITICIDE-INSECTICIDE Abamectin (ANSI) NUFARM AMERICAS 228-734 3 2A, 2B INC 228 ABBA 0.15 MAKHTESHIM-AGAN OF 66222-191 None None NORTH AMER INC ABBA 0.15 EC MITICIDE INSECTICIDE Abamectin MAKHTESHIM-AGAN OF 66222-139 3 1, 2A NORTH AMER INC ABBA ULTRA MITICIDE INSECTICIDE Abamectin (ANSI) MAKHTESHIM-AGAN OF 66222-226 3 2B NORTH AMER INC ACELLUS AZT Acetochlor; Atrazine GROWMARK INC 62719-671-534 1, 2 2C ACELLUS AZT LITE Acetochlor; Atrazine GROWMARK INC 62719-670-534 1, 2 2C ACETO BIFENTHRIN 2 EC Bifenthrin ACETO AGRICULTURAL 2749-556 1, 3 2A, 2B CHEMICALS CORP ACURON HERBICIDE Atrazine; S-metolachlor; Mesotrione; SYNGENTA CROP 100-1466 1, 2 2C Bicyclopyrone -
Calarp) Program
California Accidental Release Prevention (CalARP) Program Administering Agency Guidance January 31, 2005 Preface This document provides general guidance to help Administering Agencies (AAs) implement and enforce the California Accidental Release Prevention (CalARP) Program. The intent is to identify the elements of the Program applicable to each regulated business, and assist AAs with oversight of the CalARP Program statutes and regulations. This document is not a substitute for the CalARP Program regulations; it does not impose legally binding requirements. About This Document This document follows the format of the California Code of Regulations, Title 19, Division 2, Chapter 4.5: California Accidental Release Prevention (CalARP) Program. The regulatory sections are presented in parentheses for ease of reference. Acknowledgements The California Emergency Management Agency (Cal EMA) would like to thank the following people for their valuable assistance in the preparation of this document: Howard Wines, Hazardous Materials Specialist, City of Bakersfield Fire Department Robert Distaso P.E., Fire Safety Engineer, Orange County Fire Authority Randall L. Sawyer, Supervisor, Accidental Release Prevention Programs, Contra Costa County Health Services Department Beronia Beniamine, Senior Hazardous Materials Specialist, Stanislaus County Environmental Resources Department Angie Proboszcz, Risk Management Program Coordinator, USEPA Region 9 Jon Christenson, Senior Environmental Health Specialist, Merced County Department of Public Health Teresa -
Special Report 354 April 1972 Agricultural Experiment Station
ORTMAL DO ;10T REMOVE 7.9 m FILE Special Report 354 April 1972 Agricultural Experiment Station Oregon State University, Corvallis I FIELD APPLICATION OF HERBICIDES--AVOIDING DANGER TO FISH Erland T. Juntunen Department of Fisheries and Wildlife Oregon State University Corvallis, Oregon and Logan A. Norris Pacific Northwest Forestry Sciences Laboratory and Range Experiment Station Forest Service, U. S. Department of Agriculture Corvallis, Oregon April, 1972 Trade names are used in this publication solely to provide specific information. No endorsement of products is intended nor is criticism implieLl to products mentioned or omitted. Recommendations are not made concerning safe use of products nor is any guarantee or warranty of results or effects of the products intended or implied. ii Chemical weed and brush control with herbicides is an important land management practice in modern agriculture and forestry. In some cases, herbicides are applied directly to bodies of water for aquatic weed control. More commonly, herbicides are applied to lands adjacent to waterways for general weed and brush control. The responsible applicator will avoid damage to fishery resources by being fully aware of a particular herbicides potential hazard to fish. Herbicide applications should be considered hazardous to fish when there is the probability fish will be exposed to herbicide concen- trations which are harmful. This bulletin offers information that will aid in selecting the particular herbicides and formulations of least hazard to fish considering the toxicity of the herbicide and the poten- tial for its entry into streams, lakes, or ponds. Entry of Herbicides into the Aquatic Environment In aquatic weed control, the effective concentration of herbicide in the water depends on the rate of application, the rate of the spread of the chemical, the size and chemical composition of the body of water, the rate of degradation or adsorption of the chemical on sediments, and the rate of mixing of treated water with untreated water. -
The Spruce Budworm, Choristoneura Fumiferana
02-01370 Spruce Budworm Bro 10/10/02 11:09 AM Page 1 MORE INFORMATION The he spruce budworm, Choristoneura fumiferana For more information on Spruce Budworms call: The Tree Line Spruce (Clemens), is the most destructive and widely (204) 945-7866. Or write: Budworm distributed forest defoliator in North America. Manitoba Conservation Forestry Branch In Manitoba T Forest Health and Ecology The destructive phase of this pest is the larval or caterpillar 200 Saulteaux Crescent Winnipeg, Manitoba R3J 3W3 stage. Massive budworm outbreaks occur periodically, Web site: www.gov.mb.ca/natres/forestry/ destroying hundreds of thousands of hectares of valuable fir and spruce. Aerial view of budworm damage In eastern Canada the budworm’s preferred food is balsam fir, Photos courtesy of Canadian Forest Service, Great Lakes Forest Research Centre, white spruce and red spruce. In Manitoba, the budworm Sault Ste. Marie, Ontario and Northern Forest Research Centre, Edmonton, Alberta. feeds primarily on white spruce and balsam fir, and, less frequently, on black spruce. 02-01370 Spruce Budworm Bro 10/10/02 11:09 AM Page 2 DESCRIPTION OF LIFE STAGES LIFE CYCLE DAMAGE CONTROL The adult moth has a wingspread of The female moth lays In light and moderate infestations Various insecticides are used 21 to 30 mm. It is grey-brown in its eggs in July on the damage is restricted to a partial against the spruce budworm to colour with silvery white patches on underside of needles. loss of new foliage, particularly in protect valuable spruce and fir the forewings. Normally, the eggs the upper crown trees. -
Pharmacokinetics of Anticoagulant Rodenticides in Target and Non-Target Organisms Katherine Horak U.S
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln USDA National Wildlife Research Center - Staff U.S. Department of Agriculture: Animal and Plant Publications Health Inspection Service 2018 Pharmacokinetics of Anticoagulant Rodenticides in Target and Non-target Organisms Katherine Horak U.S. Department of Agriculture, [email protected] Penny M. Fisher Landcare Research Brian M. Hopkins Landcare Research Follow this and additional works at: https://digitalcommons.unl.edu/icwdm_usdanwrc Part of the Life Sciences Commons Horak, Katherine; Fisher, Penny M.; and Hopkins, Brian M., "Pharmacokinetics of Anticoagulant Rodenticides in Target and Non- target Organisms" (2018). USDA National Wildlife Research Center - Staff Publications. 2091. https://digitalcommons.unl.edu/icwdm_usdanwrc/2091 This Article is brought to you for free and open access by the U.S. Department of Agriculture: Animal and Plant Health Inspection Service at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in USDA National Wildlife Research Center - Staff ubP lications by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Chapter 4 Pharmacokinetics of Anticoagulant Rodenticides in Target and Non-target Organisms Katherine E. Horak, Penny M. Fisher, and Brian Hopkins 1 Introduction The concentration of a compound at the site of action is a determinant of its toxicity. This principle is affected by a variety of factors including the chemical properties of the compound (pKa, lipophilicity, molecular size), receptor binding affinity, route of exposure, and physiological properties of the organism. Many compounds have to undergo chemical changes, biotransformation, into more toxic or less toxic forms. Because of all of these variables, predicting toxic effects and performing risk assess- ments of compounds based solely on dose are less accurate than those that include data on absorption, distribution, metabolism (biotransformation), and excretion of the compound.