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Michigan Hop Management Guide 2018
2018 Michigan Hop Management Guide This material is based upon work supported by the National Institute of Food and Agriculture, U.S. Department of Agriculture, under Agreement No. 2015-09785. Any opinions, findings, conclusions, or recommendations expressed in this publication are those of the author(s) and do not necessarily reflect the view of the U.S. Department of Agriculture. 2 Table of Contents Growth Stages………………………………………………………………………………………3 Weed Management………………………………………………………………………….4-5 Herbicides………………..……………………………………………………………………….6-7 Fungicides……………………………..………………………………………………………….8-9 Insecticides…………………………..………………………………………………………10-11 Miticides…………………………………………………………………………………………….12 Pesticide Toxicity to Beneficial Insects…………………………………………..13-14 Nutrient Management Considerations…………………………………………15-19 Scouting Calendar………………………………………………………………………………20 Information presented here does not supersede the label directions. To protect yourself, others, and the environment, always read the label before applying any pesticide. Although efforts have been made to check the accuracy of information presented, it is the responsibility of the person using this information to verify that it is correct by reading the corresponding pesticide label in its entirety before using the product. The information presented here is intended as a guide for Michigan hop growers in selecting pesticides and is for educational purposes only. Labels can and do change. For current label and MSDS information, visit one of the following free online databases: greenbook.net, cdms.com, and agrian.com The efficacies of products listed have not been evaluated on hop in Michigan. Reference to commercial products or trade names does not imply endorsement by Michigan State University Extension or bias against those not mentioned. This information was compiled by Erin Lizotte and Dr. Robert Sirrine with assistance from Dr. -
Identifying the Cause of Sediment Toxicity in Agricultural Sediments: the Role of Pyrethroids and Nine Seldom-Measured Hydrophobic Pesticides ⇑ Donald P
Chemosphere 90 (2013) 958–964 Contents lists available at SciVerse ScienceDirect Chemosphere journal homepage: www.elsevier.com/locate/chemosphere Identifying the cause of sediment toxicity in agricultural sediments: The role of pyrethroids and nine seldom-measured hydrophobic pesticides ⇑ Donald P. Weston a, , Yuping Ding b, Minghua Zhang c, Michael J. Lydy b a Department of Integrative Biology, University of California, 1005 Valley Life Sciences Bldg., Berkeley, CA 94720-3140, USA b Fisheries and Illinois Aquaculture Center and Department of Zoology, Southern Illinois University, 171 Life Sciences II, Carbondale, IL 62901, USA c Department of Land, Air, and Water Resources, University of California, Davis, CA 95616, USA highlights " Monitoring fails to test for many agricultural pesticides used in any given area. " Nine seldom-analyzed pesticides (e.g., abamectin) were tested for in sediments. " One-quarter of the sediment samples were toxic to the amphipod, Hyalella azteca. " The seldom-analyzed pesticides may have contributed to toxicity in a few samples. " Pyrethroid insecticides were responsible for the vast majority of toxicity. article info abstract Article history: Few currently used agricultural pesticides are routinely monitored for in the environment. Even if Received 10 January 2012 concentrations are known, sediment LC50 values are often lacking for common sediment toxicity testing Received in revised form 16 May 2012 species. To help fill this data gap, sediments in California’s Central Valley were tested for nine hydropho- Accepted 27 June 2012 bic pesticides seldom analyzed: abamectin, diazinon, dicofol, fenpropathrin, indoxacarb, methyl para- Available online 23 July 2012 thion, oxyfluorfen, propargite, and pyraclostrobin. Most were detected, but rarely at concentrations acutely toxic to Hyalella azteca or Chironomus dilutus. -
Biodegradation of Dicofol by Microbacterium Sp. D-2 Isolated
Lu et al. Appl Biol Chem (2019) 62:72 https://doi.org/10.1186/s13765-019-0480-y ARTICLE Open Access Biodegradation of dicofol by Microbacterium sp. D-2 isolated from pesticide-contaminated agricultural soil Peng Lu* , Hong‑ming Liu and Ai‑min Liu Abstract Dicofol is an organochlorine insecticide widely used to prevent pests worldwide. Consequently, serious environmen‑ tal problems have arisen from the application of dicofol. Bioremediation is an efective solution for dicofol persistence in the environment. In this study, a bacterial strain D‑2, identifed to genus Microbacterium, capable of degrading dicofol was isolated from dicofol‑contaminated agricultural soil. This represents the frst dicofol degrading bacterium isolated from this genus. Microbacterium sp. D‑2 degraded 50 mg/L dicofol within 24 h at a rate of 85.1%. Dicofol was dechlorinated by D‑2 and the further degradation metabolite was indentifed as p,p′‑dichlorobenzophenone(DCBP). Soils inoculated with Microbacterium sp. D‑2 degraded 81.9% of the dicofol, while soils without D‑2 only degraded 20.5% of the dicofol present. This fnding suggests that strain D‑2 has great potential in bioremediation of dicofol‑ contaminated soils. Keywords: Dicofol, Biodegradation, Microbacterium sp. D‑2, Bioremediation Introduction cause acute poising of fsh and shrimp, endocrine dis- Organochlorine pesticides (OCPs) are broad spectrum ruptive properties, and chronic toxicity to other organ- insecticides with high toxicity and long residual periods isms [10–13]. Terefore, it is believed that DCF would [1]. Tey have been widely used in the control of agricul- exert a negative infuence on both animals [14, 15] and tural pests, antisepsis in industrial production and the humans [16]. -
APPENDIX G3 Diflubenzuron Rejected by OPP and ECOTOX
APPENDIX G3 Diflubenzuron Rejected by OPP and ECOTOX Rejected Abgrall, J. F. (1999). Short and Medium Term Impact of Aerial Application of Insecticide Against the Winter Moth (Operophtera Brumata L.). Revue forestiere francaise (nancy) 50: 395-404. Chem Codes: Chemical of Concern: DFZ Rejection Code: NON-ENGLISH. Aguirre-Uribe, L. A., Lozoya-Saldana, A., Luis-Jauregui, A., Quinones-Luna, S., and Juarez-Ramos, F. (1991(1992)). Field Evaluation for the Population Control of Musca Domestica (Diptera: Muscidae) in Chicken Manure With Diflubenzuron. Folia entomol mex 0: 143-151. Chem Codes: Chemical of Concern: DFZ Rejection Code: NON-ENGLISH. Akanbi, M. O. and Ashiru, M. O. (1991). Towards Integrated Pest Management of Forest Defoliators the Nigerian Situation. Xviii international congress of entomology, vancouver, british columbia, canada, 1988. For ecol manage 39: 81-86. Chem Codes: Chemical of Concern: DFZ Rejection Code: REVIEW,CHEM METHODS. Akiyama, Y., Yoshioka, N., Yano, M., Mitsuhashi, T., Takeda, N., Tsuji, M., and Matsushita, S. (1997). Pesticide Residues in Agricultural Products (F.y. 1994-1996). J.Food Hyg.Soc.Jpn. 38: 381-389 (JPN) . Chem Codes: Chemical of Concern: FNT,ACP,DZ,DDVP,MTM,CYP,EFX,FNV,FVL,PMR,MOM,BFZ,IPD,TFZ,CYF,TFY,MLN,BPH,ILL,T BA,DPHP,ES,DM,BTN,FRM,IPD,MYC,TDF,TDM Rejection Code: NON-ENGLISH. Alho, C. Jr and Vieira, L. M. (1997). Fish and Wildlife Resources in the Pantanal Wetlands of Brazil and Potential Disturbances From the Release of Environmental Contaminants. Environmental toxicology and chemistry 16: 71-74. Chem Codes: Chemical of Concern: DFZ Rejection Code: REVIEW. Ali, A. -
Proposed Interim Registration Review Decision for Imidacloprid
Docket Number EPA-HQ-OPP-2008-0844 www.regulations.gov Imidacloprid Proposed Interim Registration Review Decision Case Number 7605 January 2020 Approved by: Elissa Reaves, Ph.D. Acting Director Pesticide Re-evaluation Division Date: __ 1-22-2020 __ Docket Number EPA-HQ-OPP-2008-0844 www.regulations.gov Table of Contents I. INTRODUCTION .................................................................................................................. 4 A. Summary of Imidacloprid Registration Review............................................................... 5 B. Summary of Public Comments on the Draft Risk Assessments and Agency Responses 7 II. USE AND USAGE ............................................................................................................... 14 III. SCIENTIFIC ASSESSMENTS ......................................................................................... 15 A. Human Health Risks....................................................................................................... 15 1. Risk Summary and Characterization .......................................................................... 15 2. Human Incidents and Epidemiology .......................................................................... 17 3. Tolerances ................................................................................................................... 18 4. Human Health Data Needs ......................................................................................... 18 B. Ecological Risks ............................................................................................................ -
Laboratory Evaluation of Insect Growth Regulators Against Several Species of Anopheline Mosquitoes
[~pn.J. Sanit. 2001. Vo1. 44 No. 4 p. 349-353 19931 Laboratory evaluation of insect growth regulators against several species of anopheline mosquitoes Hitoshi KAWADA,*Yoshinori SHONO,*Takaaki ITO* and Yasuo ABE* Agricultural Science Research Center, Takarazuka Research Center, Sumitomo Chemical Co., Ltd., Takarazuka 665, Japan (Received: May 27, 1993) Key words: insecticide, insect growth regulator, pyriproxyfen, methoprene, diflubenzuron, Anopheles, vector. -- - Abstract : Larvicide efficacy of insect growth regulators (pyriproxyfen, metho- prene and diflubenzuron), in comparison with the larvicidal and adulticidal efficacy of conventional insecticides, against several species of Anopheline mosquitoes includ- ing several insecticide resistant; strains were evaluated in laboratory conditions. In all species, no cross resistance between IGRs and the other kinds of insecticides, such as organophosphate, organochlorine, carbamate and pyrethroid, was observed. Relative effectiveness of pyriproxyfen to methoprene ranged from several to 40 times and that to diflubenzuron ranged from 19.5 times to more than 400 times. In this respect, IGRs (insect growth regu- lators) seem to be useful insecticides. Pyri- proxyfen, a juvenile hormone mimic, had Anopheline mosquito is one of the most high activities to mosquitoes in the field important vectors of tropical diseases. Re- (Kawada et al., 1988; Suzuki et al., 1989; sidual spray on the wall surface and treat- Okazawa et al., 1991). In this study, we ment of breeding areas with chemicals, such evaluated the larvicide efficacy of pyriproxy- as organochlorine, organophosphate and car- fen against several species of Anopheline bamate insecticides, have been employed as mosquitoes in laboratory conditions, compar- the best and appropriate ways of controlling ing with other insecticides, and discuss the these mosquitoes. -
2019 Minnesota Chemicals of High Concern List
Minnesota Department of Health, Chemicals of High Concern List, 2019 Persistent, Bioaccumulative, Toxic (PBT) or very Persistent, very High Production CAS Bioaccumulative Use Example(s) and/or Volume (HPV) Number Chemical Name Health Endpoint(s) (vPvB) Source(s) Chemical Class Chemical1 Maine (CA Prop 65; IARC; IRIS; NTP Wood and textiles finishes, Cancer, Respiratory 11th ROC); WA Appen1; WA CHCC; disinfection, tissue 50-00-0 Formaldehyde x system, Eye irritant Minnesota HRV; Minnesota RAA preservative Gastrointestinal Minnesota HRL Contaminant 50-00-0 Formaldehyde (in water) system EU Category 1 Endocrine disruptor pesticide 50-29-3 DDT, technical, p,p'DDT Endocrine system Maine (CA Prop 65; IARC; IRIS; NTP PAH (chem-class) 11th ROC; OSPAR Chemicals of Concern; EuC Endocrine Disruptor Cancer, Endocrine Priority List; EPA Final PBT Rule for 50-32-8 Benzo(a)pyrene x x system TRI; EPA Priority PBT); Oregon P3 List; WA Appen1; Minnesota HRV WA Appen1; Minnesota HRL Dyes and diaminophenol mfg, wood preservation, 51-28-5 2,4-Dinitrophenol Eyes pesticide, pharmaceutical Maine (CA Prop 65; IARC; NTP 11th Preparation of amino resins, 51-79-6 Urethane (Ethyl carbamate) Cancer, Development ROC); WA Appen1 solubilizer, chemical intermediate Maine (CA Prop 65; IARC; IRIS; NTP Research; PAH (chem-class) 11th ROC; EPA Final PBT Rule for 53-70-3 Dibenzo(a,h)anthracene Cancer x TRI; WA PBT List; OSPAR Chemicals of Concern); WA Appen1; Oregon P3 List Maine (CA Prop 65; NTP 11th ROC); Research 53-96-3 2-Acetylaminofluorene Cancer WA Appen1 Maine (CA Prop 65; IARC; IRIS; NTP Lubricant, antioxidant, 55-18-5 N-Nitrosodiethylamine Cancer 11th ROC); WA Appen1 plastics stabilizer Maine (CA Prop 65; IRIS; NTP 11th Pesticide (EPA reg. -
THE CHEMISTRY of PESTICIDES Walter R
University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Food and Drug Administration Papers U.S. Department of Health and Human Services 6-23-1969 THE CHEMISTRY OF PESTICIDES Walter R. Benson Food and Drug Administration Follow this and additional works at: http://digitalcommons.unl.edu/usfda Part of the Dietetics and Clinical Nutrition Commons, Health and Medical Administration Commons, Health Services Administration Commons, Pharmaceutical Preparations Commons, and the Pharmacy Administration, Policy and Regulation Commons Benson, Walter R., "THE CHEMISTRY OF PESTICIDES" (1969). Food and Drug Administration Papers. 12. http://digitalcommons.unl.edu/usfda/12 This Article is brought to you for free and open access by the U.S. Department of Health and Human Services at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Food and Drug Administration Papers by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. Reproduced by the U. S. DEPARTME",T OF HEAL TI!, EDUCATION, AND WELFARE Fc·od and Drug Admilri.stration THE CHEMISTRY OF PESTICIDES Walter R. Benson Pesticide Branch, Division of Food Chemistry, Bureau of Science Food and Drug Administration, Washington, D. C. Reprinted from ANNALS OF THE NEW YORK ACADEMY OF SCIENCES Volume 160, Article 1, Pages 7-29 June 23, 1969 THE CHEMISTRY OF PESTICIDES WaIter R. Benson Pesticide.f Brallch, DivisiO/l of Food Chemistr}" Bureall of Science "-ood and Drug Administration! Washingtoll, D. C. INTRODUCTION This review is limited to the structures ana a few reactions of the pesticides mainly in~ecticides-that affect mammalian systems and that are the subject of papers by other authors in this monograph. -
Grasshopper Control in Pastures, Rangeland, and Non-Crop Areas
Grasshopper Control in Pastures, Rangeland, and Non-Crop Areas – 2002 James Robinson Extension Entomologist Texas A&M University Agricultural Research & Extension Center, Overton Grasshoppers may cause problems in Texas again this year. Pesticides labeled for hopper control in pasture, rangelands and non-crop areas are listed below. Note: the restrictions are for beef cattle only. If these products are used on a dairy, refer to the label for information on harvest and grazing. Insecticides Labeled for Grasshopper Control in Pastures or Rangeland Malathion 57 EC: Use 1 ½ to 2 pts per acre. There are no grazing or harvest restrictions. Malathion ULV: Use 8-12 fluid ounces per acre. This product is specifically designed for aircraft and ground equipment capable of applying ultra low volumes. There are no grazing or harvest restrictions. Carbaryl: Sevin 4F and Sevin XLR. Use ½ to 1 qt per acre. Restrictions: Rangeland: May be harvested or grazed the same day as application. Do not make more than one application per year. Pasture: Do not apply within 14 days of harvest or grazing. Do not exceed 3 3/4 pounds per acre per year. Up to two applications per year may be made but not more often than once every 14 days. Carbaryl: Sevin 4-Oil ULV. Use 3/8 to 1 qt per acre. For use only on rangeland. This product is not labeled for pastures. Restrictions: Do not make more than one application per year. May be harvested or grazed the same day as treatment. Do not apply more than one quart per acre per year. -
Pesticide Residues : Maximum Residue Limits
THAI AGRICULTURAL STANDARD TAS 9002-2013 PESTICIDE RESIDUES : MAXIMUM RESIDUE LIMITS National Bureau of Agricultural Commodity and Food Standards Ministry of Agriculture and Cooperatives ICS 67.040 ISBN UNOFFICAL TRANSLATION THAI AGRICULTURAL STANDARD TAS 9002-2013 PESTICIDE RESIDUES : MAXIMUM RESIDUE LIMITS National Bureau of Agricultural Commodity and Food Standards Ministry of Agriculture and Cooperatives 50 Phaholyothin Road, Ladyao, Chatuchak, Bangkok 10900 Telephone (662) 561 2277 Fascimile: (662) 561 3357 www.acfs.go.th Published in the Royal Gazette, Announcement and General Publication Volume 131, Special Section 32ง (Ngo), Dated 13 February B.E. 2557 (2014) (2) Technical Committee on the Elaboration of the Thai Agricultural Standard on Maximum Residue Limits for Pesticide 1. Mrs. Manthana Milne Chairperson Department of Agriculture 2. Mrs. Thanida Harintharanon Member Department of Livestock Development 3. Mrs. Kanokporn Atisook Member Department of Medical Sciences, Ministry of Public Health 4. Mrs. Chuensuke Methakulawat Member Office of the Consumer Protection Board, The Prime Minister’s Office 5. Ms. Warunee Sensupa Member Food and Drug Administration, Ministry of Public Health 6. Mr. Thammanoon Kaewkhongkha Member Office of Agricultural Regulation, Department of Agriculture 7. Mr. Pisan Pongsapitch Member National Bureau of Agricultural Commodity and Food Standards 8. Ms. Wipa Thangnipon Member Office of Agricultural Production Science Research and Development, Department of Agriculture 9. Ms. Pojjanee Paniangvait Member Board of Trade of Thailand 10. Mr. Charoen Kaowsuksai Member Food Processing Industry Club, Federation of Thai Industries 11. Ms. Natchaya Chumsawat Member Thai Agro Business Association 12. Mr. Sinchai Swasdichai Member Thai Crop Protection Association 13. Mrs. Nuansri Tayaputch Member Expert on Method of Analysis 14. -
Hazardous Waste Classification
HAZARDOUS WASTE CLASSIFICATION: REVIEW OF WORST CASE TO LESS WORST CASE METAL SPECIES WITH A WORKED EXAMPLE FOR A CONTAMINATED SOIL Ian Bishop 1,* and Pierre Hennebert 2 1 One Touch Data Ltd, Suite 4, Third Floor, Nicholsons House, Nicholsons Walk, Maidenhead SL6 1LD, United Kingdom 2 INERIS (National Institute for Industrial Environment and Risks), BP 2, F-60550 Verneuil-en-Halatte, France Article Info: ABSTRACT Received: The classification of waste as either hazardous or non-hazardous, especially for mix- 28 October 2020 Revised: tures such as contaminated soils, ashes, filter cakes and sludges, is not straight for- 17 February 2021 ward. In particular, as the laboratories can only measure total metal concentrations, Accepted: both the European and the UK technical guidance state that if the classifier doesn’t 25 February 2021 know exactly which metal species is in their waste, then they should start from a Available online: worst case species and use lines of evidence to work towards a more reasonable 31 March 2021 (less hazardous) species. However, the guidance doesn’t define or list worst case Keywords: nor less worst case species. While some authors have documented worst case spe- Hazardous properties cies, this is only in relation to documenting the concentrations at which each hazard Worst case Metal species property is triggered for a given worst case species. This paper addresses this gap. It documents how to define both the worst case species and more importantly, lists less worst case species for 32 elements and 204 metal species; species based on those listed in the European legislation but also supplemented by species that hav- en’t (yet) been included in this legislation but are significant nevertheless. -
Management of Fall Armyworm (Spodoptera Frugiperda), With
Management of Fall armyworm (Spodoptera frugiperda), with emphasis on Bt Transgenic Technology Galen Dively Emeritus Professor Department of Entomology University of Maryland [email protected] Outline FAW population distribution Identification, life cycle, and damage Biocontrol agents Cultural control options Biopesticides Conventional insecticides Host plant resistance with native genes Bt transgene-based resistance B.M. Prasanna, Joseph E. Huesing, Regina Eddy, Virginia M. Peschke (eds). 2018. Fall Armyworm in Africa: A Guide for Integrated Pest Management, First Edition. Mexico, CDMX: CIMMYT. Integrated management of the Fall Armyworm on maize A guide for Farmer Field Schools in Africa Food and Agriculture Organization of the United Nations, Rome, 2018 For fact sheets and management decision guides, visit:www.plantwise.org/fallarmyworm Why FAW is a serious pest in Africa: . high reproductive rate. feeds on many different crops. strong flyer, disperses long distances. continuous generations throughout the year. natural enemies do not act effectively enough to prevent crop injury. FAW Population Distribution Africa: 43 North America: 41 Central America: 28 South America: 32 Recently detected in India For countries with FAW, value at risk is over $13.3 billion and a major threat to food security. 30 – 40 days Inverted ‘Y’: 4 spots that form a square: Host plants: . Wider host range than African armyworm . Over 80 plants recorded, but prefers grasses Preferred food: . Sweet maize . Field maize . Sorghum . Bermuda grass . Grass weeds (crabgrass) Field crops: Vegetable crops: . Alfalfa . Rice . Sweet corn . Barley . Ryegrass . Sweet potato . Bermuda grass . Sorghum . Turnip Other crops: . Buckwheat . Sugarbeet . Spinach . Cotton . Sudangrass . Tomato . Apple . Clover . Soybean . Cabbage . Grape . Maize .