Agriculture indoor

It is illegal to use methyl parathion indoors. Methyl parathion is approved only for use on agricultural crops. In 1999, EPA canceled the use of methyl parathion on many food crops. 

In areas of agricultural methyl parathion usage, both outdoor and indoor air levels of methyl parathion of approximately 12 ng/m have been measured, and household dust was found to contain 21 ppb of methyl parathion. Outdoor and indoor air concentrations of methyl parathion as high as 0.71 and 9.4 pg/m, respectively, have been measured at the homes of individuals employed as pesticide formulators. 

In 1985, Berteau and Mengle (1985) of the California Department of Health Services and Maddy of the Department of Food and Agriculture conducted a preliminary review of pesticides used indoors. They noted several cases (six) from the Pesticide Illness Surveillance system in which illness was reported after structural pest control. Hypothetical exposure estimates for infants, children, and adults following label use for propoxur, DDVP, and chlorpyrifos were sometimes greater than toxic levels. In 1987, Berteau et al. (1989) reiterated the concern about the potential magnitude of indoor exposures, particularly for children. 

A 1982 guidance document of the World Health Organization (WHO, 1982) suggested use of loose-fitting, cotton, whole-body dosimeters (WBD) to overcome inefficient sample collection. The California Department of Food and Agriculture recognized the limited usefulness of patch dosimeters for determination of ADD in handler, harvester, and indoor pesticide exposure studies (Maddy et al., 1989). Whole-body dosimeters worn outside or inside standard work clothing may be a suitable means to quantitatively collect... 

Passive dosimetry, which proved useful for the pursuit of better workplace hygiene in agriculture during the past 40 years (Durham and Wolfe, 1962), yields unvalidated and excessive amounts of worker exposure (Krieger, 1996). Currently, our approach with respect to indoor and agricultural exposure assessments has been the evaluation of exposure estimates using well-known, studied chemicals to first understand the work task and at a later time develop chemical-specific studies as required in the regulatory arena. 

Bot G.P.A. (2001). Developments in indoor sustainable plant production with emphasis on energy saving. Computers and Electronics in Agriculture, 30(1-3), 151-165. 

The development of pyrethroids over the last century can be divided into two categories (1) ingredients of household insecticides for use in and around the home, emphasizing safety, and (2) photostable ingredients for outdoor use as agricultural chemicals and for larvicides of sanitary pests. Chemically stable pyrethroids, which were initially developed for outdoor use, are sometimes applied indoors. In such cases, it is absolutely essential to resolve problems, including persistent residues of such compounds indoors, and environmental issues. 

Insects have acquired resistance to organochlorine compounds, such as DDT and BHC, developed as agricultural and hygienic insecticides after World War II. This insect resistance was also acquired to subsequent organophosphorus compounds and carbamate insecticides. Photostable pyrethroids have been developed for outdoor use because pyrethroids were found to be effective against these resistant pests. As a matter of course, these pyrethroids are also effective against sanitary pests however, problems associated with safety and chemical residues indoors must be resolved. 

The main application fields of pyrethrins are limited to indoor use because of their instability to heat, light, and oxygen. Since the absolute configuration of the six insecticidal components of pyrethrins were elucidated in 1958, various researches on structural modifications have been carried out actively in many countries for more than half a century, leading to the development of a variety of photostable pyrethroids. As a result, they have been widely put into outdoor use for agriculture, forestry, animal health, termite control, and so on. 

Natural pyrethrins, insecticidal ingredients occurring in the flowers of Tanacetum cinerariaefolium (also known as Chrysanthemum cinerariaefolium or Pyrethrum cinerariaefolium), have been modified for higher stability in the environment as well as better biological performance for more than 40 years, and consequently more than 30 synthetic pyrethroids have been marketed and used worldwide for controlling indoor and agricultural pest insects [1,2]. 

EPA considers it potentially harmful to children. Indoor household use is scheduled to end in 2002, lawn and garden use in 2003. Agricultural applications will continue. 

SOIL. All consolidated earth material over bedrock. Soil is approximately equivalent to regolith.1 Agriculturally, soil is any one of many varied natural media that support or can support land plant growth outdoors or. when in containers, indoors. The lower limit of topsoil is normally the lower limit of biologic activity, which usually coinrides with the common rooting of native perennial land plants. The word soil is derived from the Latin solum for ground, ... 

Chlorpyrifos [0,0-diethyl 0-(3,5,6-trichloro-2-pyridinyl) phosphorothioate] became one of the largest selling insecticides in the world and had both agricultural and urban uses. The insecticide could be purchased for indoor use by homeowners, but health-related concerns caused USEPA to cancel home indoor and lawn application uses in 2001. The only exception is its continued use as a termiticide. 

Insecticides and fungicides used in interiors are the same as those used in agriculture and forestry, but herbicides are seldom applied indoors (Butte, Schencke and Heinzow, 2006). In contrast to the outdoor environment, where modern pesticides are degraded rather quickly by microorganisms, hydrolysis and UV light, biocides applied indoors tend to be persistent. Adsorbed to a dry and dark medium such as house dust, an abiotic degradation may hardly occur and... 

After 1983, the Standing Committee of State Council decided to stop the application of DDT in agriculture. Thereafter, DDT was mainly used as a raw material to produce Dicofol, with a small portion consumed as raw material to produce paints, as additives to produce mosquito-repellent incense, and to prevent malaria. The Chinese Center for Disease Control and Prevention (CDC) has decided that DDT can be used in closed systems and indoor sites in small amounts to control disease vectors, but its outdoor use is forbidden to prevent pollution. Malaria control in China has been effective, and DDT has not been used by local CDCs since 2001. The sale and consumption of DDT in 2001 and 2002 are shown in Table 3.4. It is seen that 83.9% of DDT produced was used to produce Dicofol 8.5% of that was exported for malaria prevention, 2.5% was used to produce mosquito-repellent incense, and 3.9% was used to produce paints. The investigation of consumption in 10 provinces and cities of China indicates that DDT is no longer used for agriculture or termite control, and a small portion of DDT is still used to prevent malaria. For example, 380 MT of DDT was used to control malaria between 1997 and 2000 in Yunnan province. 

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