Home Number °5333 D N0t Scanned
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Acifluorfen Sorption, Degradation, and Mobility in a Mississippi Delta Soil
Acifluorfen Sorption, Degradation, and Mobility in a Mississippi Delta Soil L. A. Gaston* and M. A. Locke ABSTRACT repulsion effects, acifluorfen is sorbed by soil or soil Potential surface water and groundwater contaminants include her- constituents (Pusino et al., 1991; Ruggiero et al., 1992; bicides that are applied postemergence. Although applied to the plant Pusino et al., 1993; Gennari et al., 1994b; NeÁgre et al., canopy, a portion of any application reaches the soil either directly 1995; Locke et al., 1997). Although the extent of sorp- or via subsequent foliar washoff. This study examined sorption, degra- tion in soil is generally proportional to OC content dation, and mobility of the postemergence herbicide acifluorfen (5-[2- (Gennari et al., 1994b; NeÁgre et al., 1995; Locke et al., chloro-4-(trifluoromethyl)phenoxy]-2-nitrobenzoic acid) in Dundee 1997), sorption likely involves processes other than par- silty clay loam (fine-silty, mixed, thermic, Aeric Ochraqualf) taken titioning between aqueous and organic matter phases. from conventional till (CT) and no-till (NT) field plots. Homogeneous In particular, acifluorfen forms complexes with divalent surface and subsurface samples were used in the sorption and degrada- tion studies; intact soil columns (30 cm long and 10 cm diam.) were and trivalent cations (Pusino et al., 1991; Pusino et al., used in the mobility study. Batch sorption isotherms were nonlinear 1993) that may be sorbed or precipitated. Complex for- (Freundlich model) and sorption paralleled organic C (OC) content. mation and subsequent sorption may partially account All tillage by depth combinations of soil exhibited a time-dependent for increased acifluorfen sorption with decreasing soil approach to sorption equilibrium that was well described by a two- pH or increasing cation exchange capacity (Pusino et site equilibrium±kinetic model. -
40 CFR Ch. I (7–1–18 Edition) § 455.61
§ 455.61 40 CFR Ch. I (7–1–18 Edition) from: the operation of employee show- § 455.64 Effluent limitations guidelines ers and laundry facilities; the testing representing the degree of effluent of fire protection equipment; the test- reduction attainable by the applica- ing and emergency operation of safety tion of the best available tech- showers and eye washes; or storm nology economically achievable water. (BAT). (d) The provisions of this subpart do Except as provided in 40 CFR 125.30 not apply to wastewater discharges through 125.32, any existing point from the repackaging of microorga- source subject to this subpart must nisms or Group 1 Mixtures, as defined achieve effluent limitations rep- under § 455.10, or non-agricultural pes- resenting the degree of effluent reduc- ticide products. tion attainable by the application of the best available technology economi- § 455.61 Special definitions. cally achievable: There shall be no dis- Process wastewater, for this subpart, charge of process wastewater pollut- means all wastewater except for sani- ants. tary water and those wastewaters ex- § 455.65 New source performance cluded from the applicability of the standards (NSPS). rule in § 455.60. Any new source subject to this sub- § 455.62 Effluent limitations guidelines part which discharges process waste- representing the degree of effluent water pollutants must meet the fol- reduction attainable by the applica- lowing standards: There shall be no dis- tion of the best practicable pollut- charge of process wastewater pollut- ant control technology (BPT). ants. Except as provided in 40 CFR 125.30 through 125.32, any existing point § 455.66 Pretreatment standards for existing sources (PSES). -
Synthesis of High Carbon Materials from Acetylenic Precursors
Reprinted from The Journal of Organic Chemistry, 1988, Vol. 53, page 2489 Copyright @ 1988 by the American Chemical Society and reprinted by permission of the copyright owner. Synthesis of High Carbon Materials from Acetylenic Precursors. Preparation of Aromatic Monomers Bearing Multiple Ethynyl Groups1 Thomas X. Neenan and George M. Whitesides* Department of Chemistry, Harvard University, Cambridge, Massachusetts 02138 Received October 13, 1987 The synthesis of polyethynyl aromatics as starting materials for the preparation of highly cross-linked organic solids containing high atom fractions of carbon is described. Treatment of bromo- and iodoaromatic compounds with (trimethylsily1)acetylene (TMSA) in the presence of palladium(0)and copper(1) in amine solvents yields (trimethylsily1)ethynyl-substituted aromatics. The TMS protecting groups can be removed by hydrolysis with mild base. Compounds prepared by using this technique include 1,3-diethynylbenzene,2,5-diethynylthiophene, 1,3-diethynyltetrafluorobenzene,1,4-diethynyltetrafluorobenzene, 2-ethynylthiazole, 2,4-diethynylthiazole, 2,7- diethynylnaphthalene, hexakis((trimethylsilyl)ethynyl)benzene, tetraethynylthiophene, 2,5-bis((trimethy1- silyl)ethynyl)-3,4-bis(3-hydroxy-3-methyl-l-butynyl)thiophene,2,5-diethyny1-3,4-bis(3-hydroxy-3-methyl-l-b~- tynyl)thiophene, 2,5-bis(4-(2-thienyl)butadiynyl)-3,4-bis(3-hydroxy-3-methyl-l-butynyl)thiophene,and 2,5-bis- (4-(2-thienyl)butadiynyl)-3,4-diethynylthiophene. Introduction We are engaged in a project aimed at the preparation of organic solids -
PINE RIVER CONTAMINATION SURVEY St
PINE RIVER CONTAMINATION SURVEY St. Louis, Michigan [June 2-6, 1980] October 1980 CONTENTS EXECUTIVE SUMMARY INTRODUCTION. .......................... 1 SUMMARY ............................. 2 CONCLUSIONS ........................... 2 RECOMMENDATION. ......................... 3 TECHNICAL ANALYSIS BACKGROUND. ........................... 4 STUDY METHODS .......................... 6 ANALYTICAL RESULTS. ....................... 11 TOXICITY AND HEALTH EFFECTS ................... 14 EVALUATION OF FINDINGS. ..................... 17 APPENDICES A ELUTRIATION STUDY, PINE RIVER SEDIMENT B SUMMARY OF ANALYTICAL METHODOLOGY C TOXIC DATA COMPLETION METHODS TABLES 1 River Water Sampling Stations (RWS) Locations. ....... 8 2 River Sediment Sampling (RSS) Locations. .......... 9 3 Sediment Core Descriptions ................. 10 4 River Sediment Samples (RSS) ................ 13 5 Priority Pollutants. .................... 15 FIGURE 1 River Sampling Locations . EXECUTIVE SUMMARY INTRODUCTION * A survey conducted in 1974 by the Michigan Department oc Natural Re- sources (DNR) indicated severe contamination of the Pine River sediments in ** the St. Louis, Michigan Reservoir and below the Velsicol Chemical Corpo- ration (VCC) plant site. Several organic compounds were identified in the study including: DOT and associated analogs (total DOT: 293 mg/kg), phthalates (19.5 mg/kg), polybrominated biphenyls (PBB : 9.0 mg/kg), and oils (19,000 mg/kg). Flesh analyses of Pine River fish showed high levels of PBB (0.87 mg/kg), polychlorinated biphenyls (PCB 1254: 1.99 mg/kg), and total DOT (1.65 mg/kg). A Michigan Department of Public Health warning against consumption of Pine River fish from St. Louis 60 km downstream to the confluence with the Chippewa River was issued in November 1974, because of PBB contamination. This warning was renewed in 1976 and still remains in effect. A In a publication dated June 15, 1979, concerning the contaminated Pine River the Michigan DNR recommended the following: (1) The St. -
Appendix a Analysis of Products with Two Or More Active Ingredients
APPENDIX A ANALYSIS OF PRODUCTS WITH TWO OR MORE ACTIVE INGREDIENTS The Agency does not routinely include, in its risk assessments, an evaluation of mixtures of active ingredients, either those mixtures of multiple active ingredients in product formulations or those in the applicator’s tank. In the case of the product formulations of active ingredients (that is, a registered product containing more than one active ingredient), each active ingredient is subject to an individual risk assessment for regulatory decision regarding the active ingredient on a particular use site. If effects data are available for a formulated product containing more than one active ingredient, they may be used qualitatively or quantitatively1 2. There are no product LD50 values, with associated 95% Confidence Intervals (CIs) available for glyphosate. As discussed in USEPA (2000) a quantitative component-based evaluation of mixture toxicity requires data of appropriate quality for each component of a mixture. In this mixture evaluation an LD50 with associated 95% CI is needed for the formulated product. The same quality of data is also required for each component of the mixture. Given that the formulated products for glyphosate do not have LD50 data available it is not possible to undertake a quantitative or qualitative analysis for potential interactive effects. However, because the active ingredients are not expected to have similar mechanisms of action, metabolites, or toxicokinetic behavior, it is reasonable to conclude that an assumption of dose-addition would be inappropriate. Consequently, an assessment based on the toxicity of glyphosate is the only reasonable approach that employs the available data to address the potential acute risks of the formulated products. -
Hexachlorobenzene UNITED NATIONS
UNITED NATIONS RC UNEP/FAO/RC/CRC.5/10/Add.1 Distr.: General 2 December 2008 United Nations English only Environment Programme Food and Agriculture Organization of the United Nations Rotterdam Convention on the Prior Informed Consent Procedure for Certain Hazardous Chemicals and Pesticides in International Trade Chemical Review Committee Fifth meeting Rome, 23–27 March 2009 Item 4 (b) (vii) of the provisional agenda* Listing of chemicals in Annex III to the Rotterdam Convention: review of notifications of final regulatory actions to ban or severely restrict a chemical: hexachlorobenzene Hexachlorobenzene Note by the Secretariat Addendum Supporting documentation provided by Canada The Secretariat has the honour to provide, in the annex to the present note, documentation received from Canada to support its notification of final regulatory action on hexachlorobenzene as an industrial chemical. * UNEP/FAO/RC/CRC.5/1. K0842870 161208 For reasons of economy, this document is printed in a limited number. Delegates are kindly requested to bring their copies to meetings and not to request additional copies. UNEP/FAO/RC/CRC.5/10/Add.1 Annex • Hexachlorobenzene: Priority Substances List Assessment Report, Environment Canada, Health Canada. • Environmental Assessments of Priority Substances Under the Canadian Environmental Protection Act, Guidance Manual, Version 1.0 — March 1997. Environment Canada. • SOR/2005-41; CANADIAN ENVIRONMENTAL PROTECTION ACT, 1999; Prohibition of Certain Toxic Substances Regulations, 2005, Canada Government Gazette. 2 Canadian -
Removal Rate of Herbicide Aclonifen with Isolated Bacteria and Fungi - 351
Erguven et al.: Removal rate of herbicide aclonifen with isolated bacteria and fungi - 351 - REMOVAL RATE OF HERBICIDE ACLONIFEN WITH ISOLATED BACTERIA AND FUNGI ERGUVEN, G. O.1* ‒ BAYHAN, H.2 ‒ IKIZOGLU, B.2,3 ‒ KANAT, G.2 ‒ DEMİR, G.4 1Tunceli Univesity, Faculty of Engineering, Department of Environmental Engineering, 62000, Tunceli-TURKEY 2Yildiz Technical University, Faculty of Civil Engineering, Department of Environmental Engineering, 34220, Istanbul-TURKEY 3Suleyman Demirel University, Faculty of Engineering, Department of Emvironmental Engineering, 32260, Isparta-TURKEY 4Kirklareli University, Faculty of Architechture, Department of Urban and Regional Planning, 39100, Kirklareli-TURKEY *corresponding author e-mail:[email protected] (Received 5th Nov 2015; accepted 5th Mar 2016) Abstract. In this research the microbial biodegradation of aclonifen was investigated using liquid and soil experiments with identified cultures and mixed consortia. Isolated fungi and bacteria consortia showed the highest degradation at 93% of the Chemical Oxygen Demand (COD) parameter over five days. Bacteria mix and fungi mix performed 90% and 91% degradation in five days, as COD, while 71% and 91% were active ingredients. For Total Organic Carbon (TOC) experimental results, bacteria mix, fungi mix, and bacteria and fungi mix, showed 86%, 88% and 88% respectively. Soil studies with mixed cultures of bacteria and fungi performed the most efficient degradation, at 97% after five weeks. The degradation of aclonifen by 2 ml mixed cultures showed about 63% of degradation in five weeks and 5 ml of mixed cultures showed about 90% in six weeks. Keywords: microbial biodegradation, aclonifen, mixed consortia, chemical oxygen demand, total organic carbon Introduction One of the main factors of environmental pollution is the excessive use of chemicals and pesticides, used on a global scale, to increase production and for the protection of crops. -
AP-42, Vol. 1, Final Background Document for Pesticide Application
Emission Factor Documentation for AP-42 Section 9.2.2 Pesticide Application Final Report For U.S. Environmental Protection Agency Office of Air Quality Planning and Standards Emission Inventory Branch EPA Contract No. 68-D2-0159 Work Assignment No. I-08 MRI Project No. 4601-08 September 1994 Emission Factor Documentation for AP-42 Section 9.2.2 Pesticide Application Final Report For U.S. Environmental Protection Agency Office of Air Quality Planning and Standards Emission Inventory Branch Research Triangle Park, NC 27711 Attn: Mr. Dallas Safriet (MD-14) Emission Factor and Methodology EPA Contract No. 68-D2-0159 Work Assignment No. I-08 MRI Project No. 4601-08 September 1994 NOTICE The information in this document has been funded wholly or in part by the United States Environmental Protection Agency under Contract No. 68-D2-0159 to Midwest Research Institute. It has been subjected to the Agency's peer and administrative review, and it has been approved for publication as an EPA document. Mention of trade names or commercial products does not constitute endorsement or recommendation for use. iii iv PREFACE This report was prepared by Midwest Research Institute (MRI) for the Office of Air Quality Planning and Standards (OAQPS), U.S. Environmental Protection Agency (EPA), under Contract No. 68-D2-0159, Assignment No. 005 and I-08. Mr. Dallas Safriet was the EPA work assignment manager for this project. Approved for: MIDWEST RESEARCH INSTITUTE Roy M. Neulicht Program Manager Environmental Engineering Department Jeff Shular Director, Environmental Engineering Department September 29, 1994 v vi CONTENTS LIST OF FIGURES ................................................ viii LIST OF TABLES ................................................ -
PESTICIDES Criteria for a Recommended Standard
CRITERIA FOR A RECOMMENDED STANDARD OCCUPATIONAL EXPOSURE DURING THE MANUFACTURE AND FORMULATION OF PESTICIDES criteria for a recommended standard... OCCUPATIONAL EXPOSURE DURING THE MANUFACTURE AND FORMULATION OF PESTICIDES * U.S. DEPARTMENT OF HEALTH, EDUCATION, AND WELFARE Public Health Service Center for Disease Control National Institute for Occupational Safety and Health July 1978 For sale by the Superintendent of Documents, U.S. Government Printing Office, Washington, D.C. 20402 DISCLAIMER Mention of company names or products does not constitute endorsement by the National Institute for Occupational Safety and Health. DHEW (NIOSH) Publication No. 78-174 PREFACE The Occupational Safety and Health Act of 1970 emphasizes the need for standards to protect the health and provide for the safety of workers occupationally exposed to an ever-increasing number of potential hazards. The National Institute for Occupational Safety and Health (NIOSH) has implemented a formal system of research, with priorities determined on the basis of specified indices, to provide relevant data from which valid criteria for effective standards can be derived. Recommended standards for occupational exposure, which are the result of this work, are based on the effects of exposure on health. The Secretary of Labor will weigh these recommendations along with other considerations, such as feasibility and means of implementation, in developing regulatory standards. Successive reports will be presented as research and epideiriologic studies are completed and as sampling and analytical methods are developed. Criteria and standards will be reviewed periodically to ensure continuing protection of workers. The contributions to this document on pesticide manufacturing and formulating industries by NIOSH staff members, the review consultants, the reviewer selected by the American Conference of Governmental Industrial Hygienists (ACGIH), other Federal agencies, and by Robert B. -
Recommended Classification of Pesticides by Hazard and Guidelines to Classification 2019 Theinternational Programme on Chemical Safety (IPCS) Was Established in 1980
The WHO Recommended Classi cation of Pesticides by Hazard and Guidelines to Classi cation 2019 cation Hazard of Pesticides by and Guidelines to Classi The WHO Recommended Classi The WHO Recommended Classi cation of Pesticides by Hazard and Guidelines to Classi cation 2019 The WHO Recommended Classification of Pesticides by Hazard and Guidelines to Classification 2019 TheInternational Programme on Chemical Safety (IPCS) was established in 1980. The overall objectives of the IPCS are to establish the scientific basis for assessment of the risk to human health and the environment from exposure to chemicals, through international peer review processes, as a prerequisite for the promotion of chemical safety, and to provide technical assistance in strengthening national capacities for the sound management of chemicals. This publication was developed in the IOMC context. The contents do not necessarily reflect the views or stated policies of individual IOMC Participating Organizations. The Inter-Organization Programme for the Sound Management of Chemicals (IOMC) was established in 1995 following recommendations made by the 1992 UN Conference on Environment and Development to strengthen cooperation and increase international coordination in the field of chemical safety. The Participating Organizations are: FAO, ILO, UNDP, UNEP, UNIDO, UNITAR, WHO, World Bank and OECD. The purpose of the IOMC is to promote coordination of the policies and activities pursued by the Participating Organizations, jointly or separately, to achieve the sound management of chemicals in relation to human health and the environment. WHO recommended classification of pesticides by hazard and guidelines to classification, 2019 edition ISBN 978-92-4-000566-2 (electronic version) ISBN 978-92-4-000567-9 (print version) ISSN 1684-1042 © World Health Organization 2020 Some rights reserved. -
Development of Non-Targeted Approaches to Evidence Emerging Chemical Hazard
THESE DE DOCTORAT DE ONIRIS COMUE UNIVERSITE BRETAGNE LOIRE ECOLE DOCTORALE N° 605 Biologie Santé Spécialité : Santé Publique Par Mariane POURCHET Development of non-targeted approaches to evidence emerging chemical hazard Identification of new biomarkers of internal human exposure, in order to support human biomonitoring and the study of the link between chemical exposure and human health Thèse présentée et soutenue à Nantes, le 8 octobre 2020 Unité de recherche : LABERCA UMR INRAE 1329 Rapporteurs avant soutenance : Benedikt WARTH Associate professor, University of Vienna, Vienna, Austria Katrin VORKAMP Doctor, Aarhus University, Aarhus, Denmark Development of non-targeted approaches to evidence emerging Composition du Jury : chemical hazard Président : Adrian COVACI Professor, University of Antwerp, Antwerp, Belgium ExaminateursIdentification : Benedikt of WARTHnew biomarkers Associateof internal professor, human University exposure, of Vienna, in Vienna, order Austria to support Katrin VORKAMP Doctor, Aarhus University, Aarhus, Denmark human biomonitoringJana KLANOVA and the studyProfessor, of the Masaryk link University,between Brno, chemical Czech Republic exposure and Adrian COVACI Professor, University of Antwerp, Antwerp, Belgium human health Dir. de thèse : Jean-Philippe ANTIGNAC Doctor, Oniris, Nantes, France Thèse présentée et soutenue à Nantes, le 8 octobre 2020 Unité de recherche : LABERCA UMR INRAE 1329 I would like to express my sincere gratitude to my thesis committee, Benedikt Warth, Associate professor, Department of Food Chemistry and Toxicology, University of Vienna, Austria Katrin Vorkamp, Senior researcher, Department of Environmental Science, Aarhus University, Denmark Adrian Covaci, Professor, Toxicological Centre, University of Antwerp, Belgium Jana Klánová Professor, Research Centre for Toxic Compounds in the Environment (RECETOX), Masaryk University, Brno, Czech Republic for their time in reading and evaluating this manuscript. -
An Interactive Database to Explore Herbicide Physicochemical Properties
Electronic Supplementary Material (ESI) for Organic & Biomolecular Chemistry. This journal is © The Royal Society of Chemistry 2015 Supplementary Information An interactive database to explore herbicide physicochemical properties Michael N. Gandy,a Maxime G. Corral,a,b Joshua S. Mylnea,b* and Keith A. Stubbsa* aSchool of Chemistry and Biochemistry, The University of Western Australia, Crawley, WA, 6009, Australia. E-mail: [email protected], [email protected] bARC Centre of Excellence in Plant Energy Biology, 35 Stirling Highway, Crawley, Perth 6009, Australia Materials and Methods Compound selection To gather a comprehensive list of herbicides the literature was initially surveyed and all compounds listed in previous reviews1 were incorporated. Compounds were also sourced from the World of Herbicides provided by Herbicide Resistance Action Committee and produced by Syngenta as well as from the EU pesticide database, Department of Horticulture database (University of Kentucky), Urban Integrated Pest Management database (University of Arizona) and Department of Agriculture, Forestry & Fisheries (Republic of South Africa) and the Pesticide Manual 2. A textual list of the 334 compound names follows: 2,4,5-T; 2,4-D; 2,4-DB; acetochlor; acifluorfen; aclonifen; acrolein; alachlor; allidochlor; alloxydim; ametryne; amicarbazone; amidosulfuron; aminocyclopyrachlor; aminopyralid; amiprophos-methyl; amitrole; anilofos; asulam; atrazine; azafenidin; azimsulfuron; beflubutamid; benazolin; benazolin-ethyl; benfluralin; benfuresate; bensulfuron-