BEE POISONING from Pesticides

Total Page:16

File Type:pdf, Size:1020Kb

BEE POISONING from Pesticides How to Reduce BEE POISONING From Pesticides PNW518 A Pacific Northwest Extension Publication Washington • Oregon • Idaho How to Reduce Bee Poisoning from Pesticides By D.F. Mayer, Ph.D., Washington State University Cooperative Extension entomologist, Prosser; C.A. Johansen, Ph.D., Washington State University Cooperative Extension entomologist, retired and C.R. Baird, Extension entomologist, University of Idaho CAUSES OF BEE POISONING such bees may take two to three days to die. Bee- keepers familiar with Sevin poisoning quickly Most bee poisoning occurs when insecticides are learn to recognize the “crawlers” that move about applied to crops during the blooming period. in front of the hive but are unable to fly. Dead brood Other hazards are in or in front of the hive is typical of Sevin, micro- encapsulated methyl parathion (Penncap-M), or • Drift of toxic pesticides onto adjoining crops or arsenical poisoning. When not enough hive bees weeds that are in bloom. are left to cover the brood frames or care for the • Contamination of flowering cover crops when brood, desiccation or starvation kills the larvae. In orchards are sprayed. severe cases, few bees in the hives survive, or the • Insecticidal dusts adhere to foraging bees and entire colony may be dead. ultimately become packed with the pollen onto the hind legs. Penncap-M and Sevin are espe- One forager returning to the hive with a load of cially dangerous because they may be stored contaminated pollen or nectar can cause extreme with pollen and kill newly emerged workers the agitation and death of a number of bees. Several following season. such foragers can seriously disrupt and damage • Bees drinking or touching contaminated water the colony. Often, the queen is superseded because on foliage or flowers. of the agitation of the workers, possibly aggravated • Bees collecting contaminated pollen or nectar. by a reduction in the secretion of queen substance. Queens may be affected, especially by slow-acting BEE POISONING SYMPTOMS materials such as arsenicals, Sevin, and micro- encapsulated methyl parathion (Penncap-M), The most common symptom of bee poisoning is which may be taken into the hive with pollen. the appearance of excessive numbers of dead bees Queens may behave abnormally: for instance, lay in front of the hives. Another common symptom eggs in a poor pattern. Severely weakened or is lack of foraging bees. Aggressiveness in bees queenless colonies will not live through the follow- may be caused by most pesticides. Stupefaction, ing winter. Queenlessness the following fall have paralysis, and abnormal activities of bees are com- been associated with the use of a wide variety of monly caused by chlorinated hydrocarbons and insecticides including arsenicals, Penncap-M, Sevin, organophosphorus insecticides. Regurgitation of and parathion. Typically, severe Sevin or Penncap- the honey stomach contents is often caused by poi- M poisoning makes at least half of the colonies soning with organophosphorus insecticides. Bees queenless within 30 days. may perform abnormal communication dances on the horizontal landing board at the hive entrance while under the influence of insecticide poison- BEEKEEPER-GROWER ing. Disorganized behavior patterns may lead to COOPERATION lack of recognition of affected field bees by guard bees. A major consideration for the reduction of bee poisoning is beekeeper-grower cooperation. Many Many bees poisoned with Sevin or dieldrin slow cases could be cited where a grower, simply down and appear as though they had been chilled; through ignorance of the hazard to bees, has 3 caused tremendous damage to a large number of less hazardous than aerial application because colonies. The timing or materials of the pest con- less drift of the pesticides occurs, and smaller trol program could have been modified so that little acreages are treated at one time. or no poisoning occurred. In many cases this can be done without unduly increasing the control cost • Apply certain chemicals only in late evening, or inconveniencing the grower. night, or early morning while bees are not actively foraging (generally between 6 p.m. and Beekeepers should get acquainted with the farmer 7 a.m. in the north and 8:30 p.m. to 4 a.m. in the on whose land they place hives. They should know south). Evening applications are generally less about pest-control practices and other special prob- hazardous to bees than early morning applica- lems that might occur. tions. When high temperatures cause bees to start foraging earlier or continue later than usual When the grower rents colonies for crop pollina- (5:30 a.m. to 8:00 p.m.) shift time accordingly. tion, definite verbal or written agreements can be made. One type of written contract emphasizes • Do not apply insecticides when temperatures are crop production and has the desirable effect of expected to be unusually low following treat- encouraging closer cooperation between the ment or on nights when dews occur. Residues grower and the beekeeper. Such contracts should will remain toxic to bees for a much longer time include details of the responsibility of the bee- under such conditions. keeper in providing strong and effective colonies and of the farmer in safeguarding the bees from • Do not dump unused dusts or sprays where they poisoning. In modern agriculture, the beekeeper might become a bee poisoning hazard. Some- often depends on the grower for bee forage and times bees collect any type of fine dust material the grower depends on the beekeeper for pollina- when pollen is not readily available. Under such tion. Cooperation and understanding of each conditions, they may actually carry pesticide other’s problems are essential. dusts back to the colony. • Use insecticides that are relatively nonhazardous REGULATIONS to bees whenever such choices are consistent with other pest control considerations. Many states have regulations that attempt to reduce the hazard of insecticide applications to bees. These • Choose the less hazardous insecticide formula- are based on the safest timing and bloom conditions tions. Our tests have consistently indicated dusts for given chemicals on given crops. Note: Some of are more hazardous than sprays of the same the listed pesticides have been discontinued and insecticide. Emulsifiable (liquid) formulations are no longer available or legal to use. usually have a shorter residual toxicity to bees than do wettable powders. Granular formula- tions are low in hazard to bees. REDUCTION OF BEE POISONING • Contact and ask the beekeeper to remove colo- Following are some of the ways to help reduce bee nies from the area (or keep the bees confined poisoning: during the application period) before applying hazardous pesticides when such measures are What the Pesticide Applicator Can Do feasible and of value. • Do not apply insecticides that are toxic to bees • When roadside and other weed control opera- on crops in bloom, including cover crops in tions involve 2,4-D and similar compounds on orchards and adjacent crops or interplants. With blooming plants, select the formulations or aerial application, do not turn the aircraft or derivatives known to be least harmful to bees. transport materials back and forth across blos- Our tests have shown that at maximum dosage, soming fields. Ground application is generally alkanolamine salts and isopropyl esters are more 4 toxic than other forms. Oily formulations seem phone number in printing large enough to be to be more hazardous to bees. Spraying in late read at some distance in all apiaries so you can afternoon or evening will also lessen the hazard, be contacted readily to move the colonies when since bees will not visit the blooms after they hazardous sprays are to be applied. Several regu- become curled. The only highly toxic herbicides lations concerning such marking of apiaries are are arsenicals and DNOSBP. in effect in the Pacific Northwest. • Observe State Department of Agriculture regu- • Do not move hives back into fields treated with lations aimed at reducing bee poisoning. hazardous insecticides until at least 48 to 72 hours after the application. Our tests have shown What the Grower Can Do that 50% to 90% percent of the killing of bees by insecticides occurs during the first 24 hours • Mow or beat down orchard cover crops before after application. applying sprays hazardous to bees. Treatment with 2,4-D is the best way to remove dandelion • Choose apiary sites that are relatively isolated blooms. This is especially important in relation from intensive insecticide applications and not to the first cover spray on apples, applied dur- normally subjected to drift of chemicals. Estab- ing a critical foraging period when bees will fly lish holding yards of honey bee colonies at least several miles to obtain pollen and nectar from 4 miles from orchards being treated with toxic even a few blooms of dandelion, or mustard. materials. • Blossom-thinning sprays have not been hazard- • Learn about pest control problems and programs ous to bees in Washington orchards. However, so you can develop mutually beneficial agree- Sevin used as a fruit thinner can be hazardous if ments with growers concerning pollination ser- cover crop blooms become contaminated. vice and prudent use of pesticides. • Learn the pollination requirements of the crops • Be careful how you control insect pests around you raise. Such information is not generally beekeeping storage facilities or apiaries. Vapona known for some insect-pollinated crops, such as “No Pest Strips” will also contaminate beeswax lima beans. Application of insecticides hazardous and kill bees when the combs are put in colonies to bees on these crops, or driving beekeepers out later. Use relatively low-hazard materials, such of your area by the use of insecticides on other as Sevin bait granules for ant control and pyre- blossoming crops will likely cause poor yields. thrum aerosols for fly control.
Recommended publications
  • 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,
    [Show full text]
  • Chem7988.Pdf
    This article was originally published in a journal published by Elsevier, and the attached copy is provided by Elsevier for the author’s benefit and for the benefit of the author’s institution, for non-commercial research and educational use including without limitation use in instruction at your institution, sending it to specific colleagues that you know, and providing a copy to your institution’s administrator. All other uses, reproduction and distribution, including without limitation commercial reprints, selling or licensing copies or access, or posting on open internet sites, your personal or institution’s website or repository, are prohibited. For exceptions, permission may be sought for such use through Elsevier’s permissions site at: http://www.elsevier.com/locate/permissionusematerial Chemosphere 67 (2007) 2184–2191 www.elsevier.com/locate/chemosphere Assessment of pesticide contamination in three Mississippi Delta oxbow lakes using Hyalella azteca M.T. Moore *, R.E. Lizotte Jr., S.S. Knight, S. Smith Jr., C.M. Cooper USDA-ARS National Sedimentation Laboratory, P.O. Box 1157, Oxford, MS 38655, United States Received 8 September 2006; received in revised form 27 November 2006; accepted 8 December 2006 Available online 26 January 2007 Abstract Three oxbow lakes in northwestern Mississippi, USA, an area of intensive agriculture, were assessed for biological impairment from historic and current-use pesticide contamination using the amphipod, Hyalella azteca. Surface water and sediment samples from three sites in each lake were collected from Deep Hollow, Beasley, and Thighman Lakes from September 2000 to February 2001. Samples were analyzed for 17 historic and current-use pesticides and selected metabolites.
    [Show full text]
  • Imported Fire Ant Shipper's Guide
    TEXAS DEPARTMENT OF AGRICULTURE COMMISSIONER SID MILLER PROCEDURE FOR SHIPPING IMPORTED FIRE ANT QUARANTINED ARTICLES TO IMPORTED FIRE ANT-FREE AREAS Contact the Texas Department of Agriculture prior to shipping Fire Ant Quarantined Articles to ensure compliance with state and federal IFA regulations and USDA approved quarantine treatment requirements. Treat shipments, premises and holding/shipping areas for IFA prior to compliance and shipment inspections. Recheck shipment [containers, bedding plants, balled & burlapped (B&B) trees, etc.] for IFA by observing ant activity (foraging, nesting, flying, etc.) and by baiting, beating containers or disturbing plant media. Ensure interior of truck container are thoroughly cleaned of soil, debris, and check for IFA by inspection and baiting, and treat for IFA, if necessary. Shipments to Arizona: Ship only to the Arizona Department of Agriculture (AZDA) approved holding areas. A list of AZDA approved holding areas is available at: https://agriculture.az.gov/approved-holding-areas-0. a. Each shipment must be certified for freedom from IFA (and Japanese beetle, which has similar pesticide treatment requirements). AZDA may decide to inspect the shipment on arrival. Container grown plants:* Use Immersion or Dip Treatment using bifenthrin or chlorpyrifos; Drench Treatment using bifenthrin or chlorpyrifos, or Granular Incorporation of bifenthrin, fipronil or tefluthrin. B&B tree shipments:* Use Immersion or Dip Treatment using bifenthrin or chlorpyrifos, or use Drench Treatment using chlorpyrifos. Grass sod shipments:* Use liquid bifenthrin or chlorpyrifos or granular fipronil for broadcast field applications Texas Department of Agriculture Biosecurity and Environmental Resource Management 3/16/17 Hay shipments:** Hay or straw in direct contact with soil is not eligible for movement out of the IFA quarantined area.
    [Show full text]
  • 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.
    [Show full text]
  • 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.
    [Show full text]
  • Impact of Pesticide Use on Health in Developing Countries
    Impact of pesticide use on health in developing countries Proceedings of a symposium held in Ottawa, Canada, 1 7-20 September 1990 IDRC CRDI International Development Research Centre Centre de recherches pour le devetoppement international 1 March 1993 Dear Reader/Librarian, IDRC is a public corporation created by the Canadian parliament in 1970 to help developing countries find viable solutions to their problems through research. At the 1992 Earth Summit, IDRC's mandate was broadened to emphasize sustainable development issues. As part of IDRC's strengthened commitment to global action and harüony, we are pleased to send you a complimentary copy of our most recent publication: The impact of pesticide use on health in developing countries (March 1993, 352 pages, 0-88936-560-1, $17.95). The first part of this book presents a brief survey of the global situation and the results of twelve epidemiological studies carried out by researchers from Africa, Latin America, Asia and the Middle East. These focus on poisonings resulting from organophosphates, herbicides, and pyrethroids. The second part illustrates the role of the process of development, production, spraying techniques and legislation in protecting the health of workers. A discussion of the benefits and modalities of access to pertinent information for the prevention of pesticide poisonings is provided in the third section. Finally, in the fourth section, consideration is given to the advantages and disadvantages of certain alternatives to the use of synthetic pesticides in agriculture and public health, such as botanical pesticides and integrated pest management strategies. We hope this book is a valuable addition to your collection.
    [Show full text]
  • US EPA, Pesticide Product Label, LIBERTY CHLORPYRIFOS
    law UNITED STATES ENVIRONMENTAL PROTECTIOc N AGENCY WASHINGTON, DC 20460 OFFICE OF CHEMICAL SAFETY AND POLLUTION PREVENTION «t PRO^" August 21,2014 Mr. Scott Baker . , \ Regulatory Agent Liberty Chlorpyrifos Bifenthrin 1966 W 15th Street, Suite 6 Loveland, CO 80538 Subject: Label Notification per PRN 98-10- Addition of Two Non-Public Health Pests Product Name: Liberty Chlorpyrifos Bifenthrin EPA Registration Number: 89168-20 Application Date: June 24, 2014 Decision Number: 493033 Dear Mr. Baker The Agency is in receipt of your Application for Pesticide Notification under Pesticide Registration Notice (PRN) 98-10 for the above referenced product. The Registration Division (RD) has conducted a review of this request for its applicability under PRN 98-10 and finds that the action requested falls within the scope of PRN 98-10. The label submitted with the application has been stamped "Notification" and will be placed in our records. If you have any questions, you may contact BeWanda Alexander at (703)305-7460 or via email [email protected]. Mark Soarez, Product Manager 13 Insecticide Branch Registration Division (7505P) Office of Pesticide Programs Tgjtg read iratruction* on nvone before comoi 'form. Form Approved MB No. 2070-O06O. Approval expires 2-28-85 United States Registration OPP Identifier Number Environmental Protection Agency Amendment &EPA Washington, DC 20460 Other Application for Pesticide - Section I 1. Company/Product Number 2. EPA Product Manager 3. Proposed Classification 89168-20 Gebken None Restricted 4. Company/Product (Name) PM# LIBERTY CHLORPYRIFOS BIFENTHRIN 10 5. Name and Address of Applicant (Include ZIP Code) 6. Expedited Reveiw. In accordance with FIFRA Section 3(c)(3) LIBERTY CROP PROTECTION, LLC (b)(i), my product is similar or identical in composition and labeling to: 1966 W 15th Street, Suite 6 EPA Reg.
    [Show full text]
  • INDEX to PESTICIDE TYPES and FAMILIES and PART 180 TOLERANCE INFORMATION of PESTICIDE CHEMICALS in FOOD and FEED COMMODITIES
    US Environmental Protection Agency Office of Pesticide Programs INDEX to PESTICIDE TYPES and FAMILIES and PART 180 TOLERANCE INFORMATION of PESTICIDE CHEMICALS in FOOD and FEED COMMODITIES Note: Pesticide tolerance information is updated in the Code of Federal Regulations on a weekly basis. EPA plans to update these indexes biannually. These indexes are current as of the date indicated in the pdf file. For the latest information on pesticide tolerances, please check the electronic Code of Federal Regulations (eCFR) at http://www.access.gpo.gov/nara/cfr/waisidx_07/40cfrv23_07.html 1 40 CFR Type Family Common name CAS Number PC code 180.163 Acaricide bridged diphenyl Dicofol (1,1-Bis(chlorophenyl)-2,2,2-trichloroethanol) 115-32-2 10501 180.198 Acaricide phosphonate Trichlorfon 52-68-6 57901 180.259 Acaricide sulfite ester Propargite 2312-35-8 97601 180.446 Acaricide tetrazine Clofentezine 74115-24-5 125501 180.448 Acaricide thiazolidine Hexythiazox 78587-05-0 128849 180.517 Acaricide phenylpyrazole Fipronil 120068-37-3 129121 180.566 Acaricide pyrazole Fenpyroximate 134098-61-6 129131 180.572 Acaricide carbazate Bifenazate 149877-41-8 586 180.593 Acaricide unclassified Etoxazole 153233-91-1 107091 180.599 Acaricide unclassified Acequinocyl 57960-19-7 6329 180.341 Acaricide, fungicide dinitrophenol Dinocap (2, 4-Dinitro-6-octylphenyl crotonate and 2,6-dinitro-4- 39300-45-3 36001 octylphenyl crotonate} 180.111 Acaricide, insecticide organophosphorus Malathion 121-75-5 57701 180.182 Acaricide, insecticide cyclodiene Endosulfan 115-29-7 79401
    [Show full text]
  • 2.13 Fipronil Effect on the Frequency of Anomalous Brood in Honeybee Reared in Vitro Carina A.S
    Hazards of pesticides to bees - 12th International Symposium of the ICP-PR Bee Protection Group, Ghent (Belgium), September 15-17, 2014 2.13 Fipronil effect on the frequency of anomalous brood in honeybee reared in vitro Carina A.S. Silva1, Elaine C.M. Silva-Zacarin2, Caio E.C. Domingues2, Fábio C. Abdalla2, Osmar Malaspina3, Roberta C.F. Nocelli1*. 1CCA - Centro de Ciências Agrarias, UFSCar - Universidade Federal de São Carlos. Rod. Anhanguera, SP 330, Km. 174, Araras – SP, Brasil. Email: [email protected]; Email: [email protected], *Phone: +55 (19) 3543- 2595 2LABEF – Laboratório de Biologia Estrutural e Funcional. Universidade Federal de São Carlos – UFSCar. Rodovia João Leme dos Santos (SP-264), Km. 110, Bairro Itinga, Sorocaba – SP, Brasil. 3CEIS – Centro de Estudos de Insetos Sociais. Universidade Estadual “Julio de Mesquita Filho” - UNESP. Av. 24 A, 1515, Bela Vista, Rio Claro – SP, Brasil. Abstract Larvae of honeybee workers were exposed to the insecticide fipronil during the feeding phase. To evaluate the effect of fipronil in the post-embryonic development of africanized Apis mellifera, bioassays of toxicity were done. The bioassays were performed by acute exposure applying 1μL of distilled water for control (I) and for experiments: 0.5 ng a.i./µL of fipronil; 5 ng a.i./µL of fipronil and 20 ng a.i./ µL of fipronil. Triplicates were performed for all treatments. The results showed that the rate of anomalous pupae in exposed honeybees was statistically significant in relationship to the control (p <0:03). The most frequent abnormalities were: high pigmentation on the proximal and distal larval body and body malformation, such as absence of head and limbs.
    [Show full text]
  • Western Flower Thrips Management on Greenhouse-Grown Crops
    Western Flower Thrips Management on Greenhouse-Grown Crops Greenhouse producers worldwide are familiar with the Eggs hatch in two to four days. Nymphs feed on both western flower thrips, Frankliniella occidentalis (Pergande), leaves and flowers. The first nymphal stage lasts one to one of the most destructive insect pests of greenhouse- two days; the second nymphal stage, two to four days. grown crops. Western flower thrips, the primary thrips Second instar nymphs are typically more active and tend species encountered by greenhouse producers, is extremely to feed more than first instar nymphs. The second instar polyphagous, feeding on a wide-variety of horticultural nymph eventually migrates to the plant base and enters crops grown in both commercial and research greenhouses. the growing medium to pupate. Western flower thrips also This insect pest has been included in greenhouse pest pupate in leaf debris, on the plant, and in the open flowers control brochures since 1949. It was not considered a of certain types of plants including chrysanthemum. There major insect pest of greenhouse-grown crops until the are actually two “pupal” stages: a prepupa (or propupa) and 1980s. This publication addresses biology and damage; pupa. Both stages commonly occur in growing medium or scouting; and cultural, physical, insecticidal, and biological soil underneath benches. management. The issues discussed should provide insight Growing medium or soil type and pH and pupation depth on the importance of dealing with western flower thrips may influence pupal survival. Pupation depth depends on holistically instead of solely relying on insecticides. growing medium or soil type. Pupae stages do not feed Biology and Feeding Damage and are tolerant or immune to most insecticides commonly Knowledge of biology and damage is important in applied to manage western flower thrips nymphs and understanding the challenges associated with developing adults.
    [Show full text]
  • Validation Report 28
    EURL for Cereals and Feeding stuff National Food Institute Technical University of Denmark Validation Report 28 Determination of pesticide residues in hay by LC-MS/MS and GC-MS/MS (QuEChERS method) Susan Strange Herrmann Mette Erecius Poulsen February 2018 Page 2 of 67 CONTENT: 1. Introduction ...................................................................................................................................... 3 2. Principle of analysis......................................................................................................................... 3 3. Validation design ............................................................................................................................. 4 4. Calibration curves............................................................................................................................ 4 5. Validation parameters...................................................................................................................... 4 6. Criteria for the acceptance of validation results ............................................................................. 5 7. Results and conclusion ..................................................................................................................... 6 9. References ........................................................................................................................................ 6 Appendix 1a. GCMSMS transitions used for validation of pesticides in Hay ....................................
    [Show full text]
  • RR Program's RCL Spreadsheet Update
    RR Program’s RCL Spreadsheet Update March 2017 RR Program RCL Spreadsheet Update DNR-RR-052e The Wisconsin DNR Remediation and Redevelopment Program (RR) has updated the numerical soil standards in the August 2015 DNR-RR- 052b RR spreadsheet of residual contaminant levels (RCLs). The RCLs were determined using the U.S. EPA RSL web- calculator by accepting EPA exposure defaults, with the exception of using Chicago, IL, for the climatic zone. This documentThe U.S. provides EPA updateda summary its Regionalof changes Screening to the direct-contact Level (RSL) RCLs website (DC-RCLs) in June that2015. are To now reflect in the that March 2017 spreadsheet.update, the The Wisconsin last page ofDNR this updated document the has numerical the EPA exposuresoil standards, parameter or residual values usedcontaminant in the RCL levels calculations. (RCLs), in the Remediation and Redevelopment program’s spreadsheet of RCLs. This document The providesU.S. EPA a RSL summary web-calculator of the updates has been incorporated recently updated in the Julyso that 2015 the spreadsheet.most up-to-date There toxicity were values no changes for chemi - cals madewere certainlyto the groundwater used in the RCLs,RCL calculations. but there are However, many changes it is important in the industrial to note that and the non-industrial web-calculator direct is only a subpartcontact of the (DC) full RCLsEPA RSL worksheets. webpage, Tables and that 1 andthe other 2 of thissubparts document that will summarize have important the DC-RCL explanatory changes text, generic tablesfrom and the references previous have spreadsheet yet to be (Januaryupdated.
    [Show full text]