Guidance on the Assessment of Exposure for Operators, Workers, 3 Residents and Bystanders in Risk Assessment for Plant Protection 1 4 Products

Total Page:16

File Type:pdf, Size:1020Kb

Guidance on the Assessment of Exposure for Operators, Workers, 3 Residents and Bystanders in Risk Assessment for Plant Protection 1 4 Products EFSA Journal 20YY;volume(issue):NNNN 1 GUIDANCE OF EFSA 2 Guidance on the Assessment of Exposure for Operators, Workers, 3 Residents and Bystanders in Risk Assessment for Plant Protection 1 4 Products 5 European Food Safety Authority2, 3 6 European Food Safety Authority (EFSA), Parma, Italy 7 8 ABSTRACT 9 Regulation (EC) No 1107/2009 has the purpose to ensure that the residues of the plant protection products, 10 consequent to application consistent with good plant protection practice and having regard to realistic conditions 11 of use, shall not have any harmful effects on human health. In 2010, the EFSA Panel on Plant Protection 12 Products and their Residues (PPR) prepared a Scientific Opinion on Preparation of a Guidance Document on 13 Pesticide Exposure Assessment for Workers, Operators, Bystanders and Residents (EFSA Journal 14 2010;8(2):1501), which highlighted some inconsistencies between the approaches adopted by regulatory 15 authorities. Therefore, the PPR Panel proposed a number of changes to practice in use (e.g. routine risk 16 assessment for individual PPPs should continue to use deterministic methods, and that a tiered approach to 17 exposure assessment remains appropriate; need of introducing an acute risk assessment for operators, workers 18 and bystanders, where PPPs are acutely toxic; for acute risk assessments, exposure estimates should normally be 19 based on 95th centiles of relevant data sets, whereas for longer term risk assessments, the starting point should 20 be a 75th centile). To prepare a Guidance Document an ad hoc working group was established to revise all the 21 available data and procedures to perform the operator, worker, bystander and resident risk assessment. In 22 addition to what reported in the PPR opinion, further data were made available to the working group which were 23 analysed and considered. The opinion also identifies those scenarios for which exposure estimates are least 24 satisfactory, and makes recommendations for further research that would reduce current uncertainties. A 25 calculator reflecting the content of the guidance is annexed to it, to support stakeholders in performing the 26 assessment of exposure and risk. 27 28 29 © European Food Safety Authority, 2014 30 31 KEY WORDS 32 exposure, operator, worker, bystander, resident, estimation, guidance, calculator 33 34 1 On request from European Commission, Question No EFSA-Q-2011-01062, approved on DD Month YYYY. 2 Correspondence: [email protected] 3 [If applicable] Acknowledgement: EFSA wishes to thank [the members of the Working Group on name of the WG]: name surname, name surname and name surname] [or] [the name of the WG/Network/EFSA Unit, etc.] for the preparatory work on this scientific output [and, if appropriate] [the hearing experts: name surname, name surname and name surname,] [and/or if appropriate] [EFSA staff: name surname and name surname] for the support provided to this scientific output. Suggested citation: European Food Safety Authority, 2014. Guidance on the Assessment of Exposure for Operators, Workers, Residents and Bystanders in Risk Assessment for Plant Protection Products. EFSA Journal 20YY;volume(issue):NNNN, 59 pp., doi:10.2903/j.efsa.20YY.NNNN Available online: www.efsa.europa.eu/efsajournal © European Food Safety Authority, 2014 Guidance on Pesticides Exposure Assessment of Operators, Workers, Residents and Bystanders 35 SUMMARY 36 37 (To be inserted) EFSA Journal 20YY;volume(issue):NNNN 2 Guidance on Pesticides Exposure Assessment of Operators, Workers, Residents and Bystanders 38 TABLE OF CONTENTS 39 Abstract .................................................................................................................................................... 1 40 Summary .................................................................................................................................................. 2 41 Table of contents ...................................................................................................................................... 3 42 Background as provided by the Commission ........................................................................................... 4 43 Terms of reference.................................................................................................................................... 4 44 Assessment ............................................................................................................................................... 5 45 1. Introduction ..................................................................................................................................... 5 46 2. Background Data ............................................................................................................................. 6 47 3. Definitions of exposed groups ....................................................................................................... 11 48 4. Overall approach ............................................................................................................................ 12 49 5. Default values proposed for the assessment .................................................................................. 14 50 5.1. Body weights ........................................................................................................................ 14 51 5.2. Breathing rates ...................................................................................................................... 14 52 5.3. Average air concentrations ................................................................................................... 15 53 5.4. Hectares treated per day ........................................................................................................ 15 54 5.5. Exposure durations ................................................................................................................ 16 55 5.6. Absorption values ................................................................................................................. 16 56 5.7. Default surface area of body parts ........................................................................................ 17 57 6. Methods for first tier exposure assessment .................................................................................... 17 58 6.1. Operator exposure ................................................................................................................. 17 59 6.2. Worker exposure ................................................................................................................... 23 60 6.2.1. Dermal exposure of workers ............................................................................................. 24 61 6.2.2. Dislodgeable Foliar Residue (DFR) ................................................................................. 25 62 6.2.3. Multiple Application Factor (MAF) ................................................................................. 25 63 6.2.4. Transfer Coefficient (TC) ................................................................................................. 25 64 6.2.5. Inhalation exposure of workers ........................................................................................ 27 65 7. Resident and bystander exposure................................................................................................... 28 66 7.1. Resident exposure ................................................................................................................. 30 67 7.1.1. Spray drift ......................................................................................................................... 30 68 7.1.2. Vapour .............................................................................................................................. 32 69 7.1.3. Surface deposits ................................................................................................................ 32 70 7.1.4. Entry into treated crops ..................................................................................................... 34 71 7.2. Bystander exposure ............................................................................................................... 35 72 7.2.1. Spray drift ......................................................................................................................... 35 73 7.2.2. Vapour .............................................................................................................................. 36 74 7.2.3. Surface deposits ................................................................................................................ 36 75 7.2.4. Entry into treated crops ..................................................................................................... 37 76 Conclusions ............................................................................................................................................ 39 77 Recommendations .................................................................................................................................. 39 78 References .............................................................................................................................................. 40 79 Appendices ............................................................................................................................................. 43 80 A. Cipac formulation codes ...............................................................................................................
Recommended publications
  • 2,4-Dichlorophenoxyacetic Acid
    2,4-Dichlorophenoxyacetic acid 2,4-Dichlorophenoxyacetic acid IUPAC (2,4-dichlorophenoxy)acetic acid name 2,4-D Other hedonal names trinoxol Identifiers CAS [94-75-7] number SMILES OC(COC1=CC=C(Cl)C=C1Cl)=O ChemSpider 1441 ID Properties Molecular C H Cl O formula 8 6 2 3 Molar mass 221.04 g mol−1 Appearance white to yellow powder Melting point 140.5 °C (413.5 K) Boiling 160 °C (0.4 mm Hg) point Solubility in 900 mg/L (25 °C) water Related compounds Related 2,4,5-T, Dichlorprop compounds Except where noted otherwise, data are given for materials in their standard state (at 25 °C, 100 kPa) 2,4-Dichlorophenoxyacetic acid (2,4-D) is a common systemic herbicide used in the control of broadleaf weeds. It is the most widely used herbicide in the world, and the third most commonly used in North America.[1] 2,4-D is also an important synthetic auxin, often used in laboratories for plant research and as a supplement in plant cell culture media such as MS medium. History 2,4-D was developed during World War II by a British team at Rothamsted Experimental Station, under the leadership of Judah Hirsch Quastel, aiming to increase crop yields for a nation at war.[citation needed] When it was commercially released in 1946, it became the first successful selective herbicide and allowed for greatly enhanced weed control in wheat, maize (corn), rice, and similar cereal grass crop, because it only kills dicots, leaving behind monocots. Mechanism of herbicide action 2,4-D is a synthetic auxin, which is a class of plant growth regulators.
    [Show full text]
  • Growth Regulation and Other Secondary Effects of Herbicides Edivaldo D
    Weed Science 2010 58:351–354 Growth Regulation and Other Secondary Effects of Herbicides Edivaldo D. Velini, Maria L. B. Trindade, Luis Rodrigo M. Barberis, and Stephen O. Duke* As all herbicides act on pathways or processes crucial to plants, in an inhibitory or stimulatory way, low doses of any herbicide might be used to beneficially modulate plant growth, development, or composition. Glyphosate, the most used herbicide in the world, is widely applied at low rates to ripen sugarcane. Low rates of glyphosate also can stimulate plant growth (this effect is called hormesis). When applied at recommended rates for weed control, glyphosate can inhibit rust diseases in glyphosate-resistant wheat and soybean. Fluridone blocks carotenoid biosynthesis by inhibition of phytoene desaturase and is effective in reducing the production of abscisic acid in drought-stressed plants. Among the acetolactate synthase inhibitors, sulfometuron-methyl is widely used to ripen sugarcane and imidazolinones can be used to suppress turf species growth. The application of protoporphyrinogen oxidase inhibitors can trigger plant defenses against pathogens. Glufosinate, a glutamine synthetase inhibitor, is also known to improve the control of plant diseases. Auxin agonists (i.e., dicamba and 2,4-D) are effective, low-cost plant growth regulators. Currently, auxin agonists are still used in tissue cultures to induce somatic embryogenesis and to control fruit ripening, to reduce drop of fruits, to enlarge fruit size, or to extend the harvest period in citrus orchards. At low doses, triazine herbicides stimulate growth through beneficial effects on nitrogen metabolism and through auxin-like effects. Thus, sublethal doses of several herbicides have applications other than weed control.
    [Show full text]
  • Carpenter Ants and Control in Homes Page 1 of 6
    Carpenter Ants and Control in Homes Page 1 of 6 Carpenter Ants and Control in Homes Fact Sheet No. 31 Revised May 2000 Dr. Jay B Karren, Extension Entomologist Alan H. Roe, Insect Diagnostician Introduction Carpenter ants are members of the insect order Hymenoptera, which includes bees, wasps, sawflies, and other ants. Carpenter ants can be occasional pests in the home and are noted particularly for the damage they can cause when nesting in wood. In Utah they are more of a nuisance rather than a major structural pest. Carpenter ants, along with a number of other ant species, utilize cavities in wood, particularly stumps and logs in decayed condition, as nesting sites. They are most abundant in forests and can be easily found under loose bark of dead trees, stumps, or fallen logs. Homeowners may bring them into their homes when they transport infested logs from forests to use as firewood. Description Carpenter ants include species that are among the largest ants found in the United States. They are social insects with a complex and well-defined caste system. The worker ants are sterile females and may occur in different sizes (majors and minors). Members of the reproductive caste (fertile males and females) are usually winged prior to mating. All ants develop from eggs deposited by a fertilized female (queen). The eggs hatch into grub-like larvae (immatures) which are fed and cared for by the workers. When fully grown, the larvae spin a cocoon and enter the pupal stage. The pupal stage is a period of transformation from the larva to adult.
    [Show full text]
  • EUPT-CF10-Webinar
    Results of EUPT-CF10 Incurred and spiked pesticides in rye Mette Erecius Poulsen Holte, 20 September 2016 PTs on cereals/feed 2016 EUPT-CF10 Test material Rye flour Participants 178 (160) Compulsory target pesticides 134 Voluntary target pesticides 7 Incurred pesticides 10 Spiked pesticides 8 Total no. of pesticides 18 National Food Institute, Technical University of Denmark Advisory Group Quality Group Amadeo R. Fernández-Alba Antonio Valverde André de Kok Stewart Reynolds Antonio Valverde Magnus Jezussek Michelangelo Anastassiades Miguel Gamón Organising team at EURL Philippe Gros Mette Erecius Poulsen Ralf Lippold Susan Strange Herrmann Sonja Masselter Parvaneh Hajeb Stewart Reynolds Merete B. Ludwigsen Tuija Pihlström Lisbet Pilhkjær Finbarr Oregan Jens-Ole Frimann National Food Institute, Technical University of Denmark National Food Institute, Technical University of Denmark Activity Dates Announcement Calendar December 2015 Target Pesticide List EUPT-Registration Website 11 January 2016 Deadline for registration 1 February 2016 Release of Specific Protocol 29 February 2016 Distribution of Test items 7 March 2016 Deadline for Receipt and Acceptance of Test Materials within 24 hr on reciept 11 April 2016 Deadline for Result Submission at 13.00 CET Deadline for submission of additional method information for 15 April 2015 false negative results Preliminary Report (only compilation of results) 30 May 2015 Final Report December 2015 National Food Institute, Technical University of Denmark Target list - new pesticides and voluntary compounds
    [Show full text]
  • Silverfish and Firebrats
    SilverfiSh and firebratS Integrated Pest Management In and Around the Home If items on your bookshelf have Although small nymphs (those that are chewed-on pages and bindings, sus- less than 1/8 inch long) lack scales, both pect the look-alike household pests large nymphs and adults have them. If silverfish and firebrats. Both insects you see scales around or beneath dam- have enzymes in their gut that digest aged items, it is a good indication that cellulose, and they choose book cases, these pests are the culprits. The scales closets, and places where books, cloth- are delicate, dustlike, and slightly in- ing, starch, or dry foods are available. candescent in the light, and they stick to most surfaces. Silverfish and firebrats are nocturnal and hide during the day. If the object LIFE CYCLE Figure 1. Adult firebrat (left) and silver- they are hiding beneath is moved, they fish. Eggs of both species are about 1/25 of will dart toward another secluded an inch long. The females lay the eggs place. They come out at night to seek in crevices, on cloth, or buried in food food and water. Both insects prefer or dust. The average clutch contains 50 dry food such as cereals, flour, pasta, eggs, but this can vary from 1 to 200. and pet food; paper with glue or paste; Firebrat eggs hatch in about 14 days and sizing in paper including wall paper; silverfish eggs in about 19 to 32 days. In book bindings; and starch in cloth- colder environments eggs can remain ing.
    [Show full text]
  • Pesticides Registration List 2018
    Pesticides Registration List 2018 Name of Chemicals Type Common Name Registration Types Registrant Syngenta AGROIN, 39,Broad Street, Charlestown, Georgetown, Guyana. 592 -689-4624 and 611-3890 Importer/Distributor Actara 25WG Insecticide Thiamethoxam General Use Actellic 50Ec Insecticide Pirimiphos methyl General Use Cruiser 350FS Insecticide Thiamethoxam General Use Demand 2.5CS Insecticide Thiamethoxam & Lambda Cyhalothrin General Use Demon MaX Insecticide Cypermethrin General Use Engeo Insecticide Thiamethoxam & Lambda Cyhalothrin General Use Match 50EC Insecticide Lufenuron General Use Ninja 5EC Insecticide Lambda Cyhalothrin General Use Pegasus 500Sc Insecticide Diafenthiuron General Use Trigard 75WP Insecticide Cyromazine General Use Vertimec 1.8EC Insecticide Abamectin General Use Dual Gold 960EC Herbicide S-Metolachlor General Use Fusilade Herbicide Fluazifop-p-butyl General Use Gramoxone Super Herbicide Paraquat Dichloride Restricted Use Igran 500SC Herbicide Terbutryn General Use Krismat Herbicide Ametryn General Use Reglone Herbicide Diquat Dibromide General Use Touchdown IQ Herbicide Glyphosate General Use Amistar 50WG Fungicide Azoxystrobin General Use Bankit 25 SC Fungicide Azoxystrobin General Use Daconil 720Sc Fungicide Chlorothalonil General Use Tilt 250 EC Fungicide Propiconazole General Use Klerat Wax Blocks Rodenticide Brodifacoum General Use Registrant Rotam Agrochemical Co., Ltd AGROIN, 39,Broad Street, Charlestown, Georgetown, Guyana. 592 -689-4624 and 611-3890 Importer/Distributor Saddler 35 FS Insecticide Thiodicarb
    [Show full text]
  • A Novel Role of Ethephon in Controlling the Noxious Weed Ipomoea Cairica
    www.nature.com/scientificreports OPEN A novel role of ethephon in controlling the noxious weed Ipomoea cairica (Linn.) Sweet Received: 09 April 2015 1,* 1,* 1,3,* 2 1 Accepted: 22 May 2015 Zhong-Yu Sun , Tai-Jie Zhang , Jin-Quan Su , Wah Soon Chow , Jia-Qin Liu , 1 1 3 1 Published: 18 June 2015 Li-Ling Chen , Wei-Hua Li , Shao-Lin Peng & Chang-Lian Peng Several auxin herbicides, such as 2, 4-D and dicamba, have been used to eradicate an exotic invasive weed Ipomoea cairica in subtropical China, but restraining the re-explosion of this weed is still a challenge. Since ethylene is one of the major intermediate functioning products during the eradication process, we explored the possibility, mechanism and efficiency of using ethephon which can release ethylene to control Ipomoea cairica. The results of the pot experiment showed that 7.2 g /L ethephon could totally kill Ipomoea cairica including the stems and roots. The water culture experiment indicated that ethephon released an abundance of ethylene directly in leaves and caused increases in electrolyte leakage, 1-aminocyclopropane-1-carboxylic acid (ACC), abscisic acid (ABA) and H2O2 and decreases in chlorophyll content and photosynthetic activity, finally leading to the death of Ipomoea cairica. The field experiment showed that the theoretical effective concentration of ethephon for controlling Ipomoea cairica (weed control efficacy, WCE = 98%) was 4.06 g/L and the half inhibitory concentration (I50) was 0.56 g/L. More than 50% of the accompanying species were insensitive to the phytotoxicity of ethephon. Therefore, ethephon is an excellent alternative herbicide for controlling Ipomoea cairica.
    [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]
  • Signs and Symptoms of Pesticide Poisoning
    University of Nebraska - Lincoln DigitalCommons@University of Nebraska - Lincoln Historical Materials from University of Nebraska-Lincoln Extension Extension 1997 EC97-2505 Signs and Symptoms of Pesticide Poisoning Larry D. Schulze University of Nebraska - Lincoln, [email protected] Clyde Ogg University of Nebraska - Lincoln, [email protected] Edward F. Vitzthum University of Nebraska - Lincoln, [email protected] Follow this and additional works at: https://digitalcommons.unl.edu/extensionhist Part of the Agriculture Commons, and the Curriculum and Instruction Commons Schulze, Larry D.; Ogg, Clyde; and Vitzthum, Edward F., "EC97-2505 Signs and Symptoms of Pesticide Poisoning" (1997). Historical Materials from University of Nebraska-Lincoln Extension. 1225. https://digitalcommons.unl.edu/extensionhist/1225 This Article is brought to you for free and open access by the Extension at DigitalCommons@University of Nebraska - Lincoln. It has been accepted for inclusion in Historical Materials from University of Nebraska-Lincoln Extension by an authorized administrator of DigitalCommons@University of Nebraska - Lincoln. University of Nebraska Cooperative Extension EC97-2505-A Signs and Symptoms of Pesticide Poisoning Larry D. Schulze, Extension Pesticide Coordinator Clyde L. Ogg, Extension Assistant, Pesticide Training Edward F. Vitzthum, Coordinator, Environmental Programs z Manage Your Risk z Signal Words z Read the pesticide Label z Routes of Exposure z Pesticide Toxicity z Recognizing Signs and Symptoms of Poisoning z Recognizing Common pesticide Poisonings { Organophosphate and Carbamate Insecticides { Organochlorine Insecticides { Synthetic Pyrethroid Insecticides { Plant-derived Insecticides { Inorganic Insecticides { Microbial Insecticides { DEET Repellent { Bipyridyl Herbicides { Chlorophenoxy Herbicides { Arsenical Herbicides { Wood Preservatives { Fumigants { Rodenticides { Fungicides z What To Do When Pesticide Poisoning Occurs z References z Pesticide Safety Telephone Numbers Accidental exposure or overexposure to pesticides can have serious implications.
    [Show full text]
  • Tetramethrin CAS #: 7696-12-0
    Review Date: 12/10/2010 tetramethrin CAS #: 7696-12-0 Type Contact insecticide - sythetic pyrethroid. Controls Flying and crawling insects such as wasps, hornets, cockroaches, ants, fleas, and mosquitos. Mode of Action Tetramethrin effects the central and peripheral nervous system by modulation of the sodium channel resulting in hyperactivity of the nervous system and death. Thurston County Review Summary: The insecticide active ingredient tetramethrin is rated high in hazard by Thurston County's review criteria for carcinogenicity and due to the risk of toxicity to children following specific indoor aerosol uses. Products containing tetramethrin fail the County's review. Tetramethrin is considered low in hazard for the potential to move off the site of application, persistence, and bioaccumulation potential. It is also considered low in hazard for the risk of toxicity to non-target organisms (except insects) - even though it is very highly toxic to fish and other aquatic organisms. MOBILITY Property Value Reference Rating Water Solubility (mg/L) 1.83 1 Low Soil Sorption (Kd=mL/g) Not found Organic Sorption (Koc=mL/g) 1423 1 Moderate Mobility Summary: Tetramehtrin is not very soluble in water and adheres moderately to soil containing organic material. Because tetramethrin is not likely to persist more than one day and adheres moderately to soil, the hazard of tetramethrin to move off the site of application is rated low. PERSISTENCE Property Value Reference Rating Vapor Pressure (mm Hg) 0.0000071 1 High Biotic or Aerobic Half-life (days) 3 1 Low Abiotic Half-life (days) 0.32 1 Low Terrestrial Field Test Half-life (days) <1 2 Low Hydrolysis Half-life (days) 1 (pH = 7) 2 Low Anaerobic Half-life (days) Not found Aquatic Field Test Half-life (days) 1 or less 2 Low Persistence Summary: Tetramethrin is very susceptable to degradation by sunlight and interaction with water.
    [Show full text]
  • Ten Reasons Not to Use Pesticides
    JOURNAL OF PESTICIDE REFORM/ SUMMER 2006 • VOL. 26, NO. 2 PESTICIDE BASICS contaminated with pesticides. They play in ways that in- crease their exposure. Also, their growing bodies can be Ten Reasons Not to Use particularly sensitive. EPA succinctly summarizes the reasons why children should not be Pesticides exposed to pesticides: • their internal organs are still BY CAROLINE COX has written, “the range of these adverse developing and maturing, health effects includes acute and persis- • in relation to their body weight, tent injury to the nervous system, lung infants and children eat and drink damage, injury to reproductive organs, more than adults, possibly increasing 1. Pesticides don’t solve pest dysfunction of the immune and endo- problems. They don’t change their exposure to pesticides in food crine [hormone] systems, birth defects, and water. the conditions that encourage and cancer.”3 pests. • certain behaviors--such as play- Pesticides that damage human ing on floors or lawns or putting Some pesticides are remarkably ef- health are used in staggering amounts. objects in their mouths—increase a ficient tools for killing pests, but almost Consider just the 27 most commonly 4 child’s exposure to pesticides used in all do nothing to solve pest problems. used pesticides. Fifteen of these have 8 5 homes and yards. To solve a pest problem, the most been classified as carcinogens by EPA Researchers continue to gather de- important step is to change the con- and their use totals about 300 million 4 tailed evidence that EPA’s concerns ditions that have allowed the pest to pounds every year.
    [Show full text]
  • 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 ................................................
    [Show full text]