Pesticide categories

Table 3.1 Pesticide categories and their label markings...

INTRODUCTION 14 PESTICIDE CATEGORIES 15 PESTICIDE HANDLERS 15 Agricultural Pesticide Handlers 15 Tasks Performed by an Individual 16 Factors Affecting Exposure 16 Residential and Institutional Pesticide Handlers 18 Families of Pesticide Handlers 19 STUDY DESIGN CONSIDERATIONS 20 Worker Stratification 21 Routes of Exposure 21 Respiratory Exposure 21 Dermal Exposure 21 Sampling Strategy Selection 21 Statistical Analysis 22 PROTECTION OF HUMAN SUBJECTS 22 PESTICIDE EXPOSURE MONITORING METHODS 23 Passive Dosimetry 23... 

The urine of randomly selected men in agricultural environments of reproductive age was analyzed for parent compounds and metabolites of pesticides and was compared with sperm concentration. The results showed that those exposed to mixtures of organophosphates and pyrethroids had lower sperm concentrations, and that sperm concentration was related to the exposure levels of the two pesticide categories, 19 ... 

Protective Percent of Farmers Using Gear for Pesticide Category ... 

Part 454 gum and wood chemicals manufacturing point source category Part 455 pesticide chemicals... 

Pesticides include the broad categories of insecticides, fungicides, rodenticides, and herbicides. Insecticides in common use fall into three categories. The chloroinsec-ticides have chlorine in their structure. They are less soluble than the other insecticide forms and much less biodegradable (i.e., more persistent). While they are less acutely toxic, several have been identified as potential carcinogens. Carbamatea are a relatively new form of pesticide. They are less persistent and less... 

AC filtration does remove some organic chemicals that can be harmful if present in quantities above the EPA Health Advisory Level (HAL). Included in this category are trihalomethanes (THM), pesticides, industrial solvents (halogenated... 

Provides access to detailed information on all categories of pesticides including herbicides, fungicides, insecticides, and rodenticides. Included is information on pesticide toxicity, health effects, residual data, efficacy, and other information. NPIC is a cooperative effort of the U.S. EPA and the Oregon State University Department of Agricultural Chemistry. NPIC is staffed from 6 30 a.m to 4 30 p.m. Pacific Standard Time. 

Manufacturers and specialist materials development associations publish extensive corrosion data in the form of monographs, and this form of presentation is also used in national standards. The most recent comprehensive text in this category is perhaps the publication by the Zinc Development Association . The work is important in that the section on chemicals also deals with common, though complex, chemical formulations, e.g. Are-extinguisher fluids, soaps and syndets, agricultural chemicals such as pesticides and fertilisers. This publication also demonstrates the mammoth task of recording all the available data for just one material. A comparable book for mild steel would probably be much larger, whereas for many other materials the information has not yet been determined. Thus at best, only very incomplete data are available in this form. 

EPA. 1985c. Pesticide chemicals category effluent limitations guidelines, pretreatment standards, and new source performance standards. U.S. Environmental Protection Agency. Federal Register 51 40672-40777. 

This far into a nitrosamine symposium it should hardly be necessary to point out that nitrosamines are technically just one of a group of Ji-nitroso compounds that also includes nitros-amides, nitrosocarbamates, nitrosoureas, etc. Or that nitrosa-table pesticides encompass all the categories just mentioned and more. Or that many diverse pesticides, including herbicides, insecticides, and fungicides have been converted to Ji-nitroso derivatives in the laboratory (a recent review contained a 3-page, probably incomplete, compilation), or that some of the Ji-nitroso compounds thus synthesized were determined to be carcinogenic in test animals or mutagenic in various assays. 

Hard evidence for the first category seems to be nonexistent. An educated guess on the potential hazards would combine residue technology [how much of a secondary amine (or amide, urea, carbamate, etc.) might a person consume or otherwise be exposed to ], nitrosation chemistry (what would be the yield of in vivo nitrosation of the pesticide thus consumed ), and toxicology (what would be the toxicological effect and potency of the nitroso compound thus formed ). Frequently, these questions, which simplify to, "What dose—eg., in mg/kg—of a pesticide-derived nitroso compound might a person be exposed to and what would be the result if he were " are not carefully considered. 

Polar or thermally labile compounds - many of the more modern pesticides fall into one or other of these categories - are not amenable to GC and therefore LC becomes the separation technique of choice. HPLC columns may be linked to a diode-array detector (DAD) or fluorescence detector if the target analyte(s) contain chromophores or fluorophores. When using a DAD, identification of the analyte(s) is based on the relative retention time and absorption wavelengths. Similarly, with fluorescence detection, retention time and emission and absorption wavelengths are used for identification purposes. Both can be subject to interference caused by co-extractives present in the sample extract(s) and therefore unequivocal confirmation of identity is seldom possible. 

Fluorescent lamps, fluorescent lamp ballasts, batteries, pesticides, mercury-containing thermostats, and other mercury-containing equipment are being singled out for special consideration. Specifically, these electrical and electronic wastes outfall into a regulated category called universal wastes in the United States. 

Newborns are especially vulnerable to pesticides effects, since they do not have a fully developed immune system and adaptation mechanisms, or detoxification systems for foreign chemicals. A direct correlation between overall pesticide exposure in a given territory and primary illness in newborns [A101] was traced into even those territories of the Ukraine where the volumes of pesticides used were not extreme. The clearest expression of the pesticide exposure - primary newborn illness correlation is seen with pesticides of the second risk class (by toxicity), while the correlation is less clear for pesticides of the third and fourth categories. The most dangerous pesticides of all types for newborns are OCPs, with OPPs a close second [A101]. 

With the LCA analysis, the impact categories - the impact on climate, water pollution and air pollution - are mostly evaluated. Whereas, impacts such as biodiversity or pesticide toxicity are seldom evaluated because of methodological problems [34]. The LCA study consists of four basic stages Definition of objectives and the scope, Inventory, Impact assessment and Interpretation [32]. 

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