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Chlorinated lindane

Reductive DechIorina.tion. Such reduction of chlorinated aUphatic hydrocarbons, eg, lindane, has been known since the 1960s. More recentiy, the dechlorination of aromatic pesticides, eg, 2,4,5-T, or pesticide products, eg, chlorophenols, has also been documented (eq. 10) (20). These reactions are of particular interest because chlorinated compounds are generally persistent under aerobic conditions. [Pg.216]

Reductive dechlorination of chlorinated aUphatic hydrocarbons, eg, lindane (11) (eq. 17) is extremely facile and occurs almost exclusively via chemical mechanisms, although microorganisms are typically the source of electron donors (30). [Pg.219]

Chemistry and Environmental Impact. Lindane is produced by the photocataly2ed addition of chlorine to ben2ene to give a mixture of isomers. The active y-HCH isomer can be preferentially extracted and purified. Composition of the technical-grade product is a (65—70%), B (7—10%), y (14—15%), 5 (7%), and S (1—2%). Lindane has been produced worldwide for its use as an insecticide and for other minor uses in veterinary, agricultural, and medical products. [Pg.67]

A limited number of pure substances are available from NIST, primarily clini-cally-relevant compounds such as cholesterol, urea, uric acid, creatinine, glucose, cortisol, tripalmitin, and bilirubin (NIST SRM website). These compounds are certified for purity (greater than 99 %) and are used as primary calibrants in definitive methods for these clinical analytes (see below). Several additional pure substances are available for specific applications such as microchemistry, i.e. elemental composition (acetanilide, anisic acid, cystine nicotinic acid, o-bromobenzoic acid, p-fluoro-benzoic acid, m-chlorobenzoic acid), polarimetric standards (sucrose and dextrose), acidimetric standard (benzoic acid and boric acid). Only three pure substance NIST RMs are available for environmental contaminants, namely the chlorinated pesticides, lindane, 4,4 -DDT, and 4,4 -DDE. [Pg.85]

Fig. 5. Relationship between the distribution (partition) coefficient on dimethyl dihydrogenated tallow montmorillonite for a range of non-ionic organic pollutants and their corresponding solubility in water. BHC is benzene hexachloride, the y-isomer of which is known as lindane aroclor 1232 and aroclor 1252 denote mixtures of polychlorinated biphenyls containing about 32 and 52% chlorine, respectively. After Beall (2003). Fig. 5. Relationship between the distribution (partition) coefficient on dimethyl dihydrogenated tallow montmorillonite for a range of non-ionic organic pollutants and their corresponding solubility in water. BHC is benzene hexachloride, the y-isomer of which is known as lindane aroclor 1232 and aroclor 1252 denote mixtures of polychlorinated biphenyls containing about 32 and 52% chlorine, respectively. After Beall (2003).
Aspila et al. [338] reported the results of an interlaboratory quality control study in five laboratories on the electron capture gas chromatographic determination of ten chlorinated insecticides in standards and spiked and unspiked seawater samples (lindane, heptachlor, aldrin, 5-chlordane, a-chlordane, dield-rin, endrin, p, p -DDT, methoxychlor, and mirex). The methods of analyses used by these workers were not discussed, although it is mentioned that the methods were quite similar to those described in the water quality Branch Analytical Methods Manual [339]. Both hexane and benzene were used for the initial extraction of the water samples. [Pg.418]

Terrence Collins is the Thomas Lord Professor of Chemistry at Carnegie Mellon University who contends that the dangers of chlorine chemistry are not adequately addressed by either academe or industry, and alternatives to chlorine and chlorine processors must be pursued. He notes, Many serious pollution episodes are attributable to chlorine products and processes. This information also belongs in chemistry courses to help avoid related mistakes. Examples include dioxin-contaminated 2,4,5-T, extensively used as a peacetime herbicide and as a component of the Vietnam War s agent orange chlorofluorocarbons (CFCs) polychlorinated biphenyls (PCBs the pesticides aldrin, chlordane, dieldrin, DDT, endrin, heptachlor, hexachlorobenzene, lindane, mirex, and toxaphene pentachlorophe-... [Pg.18]

Most of the well-known chlorinated hydrocarbon insecticides will kill horseflies and the percentages required are small. But none of them will protect livestock adequately from horseflies, as the bites are made and the damage done before these relatively slow acting materials take effect. Probably most horseflies attacking an animal sprayed with DDT, lindane, chlordan, or toxaphene (chlorinated camphene) would eventually die, but the fly reduction thereby made in an area would be insignificant unless all hosts both wild and domestic were treated frequently. [Pg.98]

Chlorinated micropoUutants are harmful for man and environment due to their toxicity, persistence, and bioaccumulation. Persistent compounds are very stable and difficult to get metabolized and mineralized by biological and chemical processes in the environment, and as a result, they have become ubiquitous in water, sediments, and the atmosphere bioaccumulation is the result of the lipophilicity of these compounds. Polychlorinated dibenzodioxins and -furans (PCDD/F) are not produced purposely like many of other chlorinated technical products, such as chlorinated biocides DDT, lindane, and toxaphene. The production and use of persistent organic pollutants (POPs), the dirty dozen has now been banned worldwide by the Stockholm protocol. It should be mentioned that about 3000 halogenated products have now been isolated as natural products in plants, microorganisms, and animals," but the total amount of these products is much smaller compared to xenobiotics. [Pg.171]

In weakly basic media, lindane undergoes /rarts-dehydrochlorination of the axial chlorines to give the intermediate 1,3,4,5,6-pentachlorocyclohexane. This compound reacts with water forming 1,2,4-trichlorobenzene, 1,2,3-trichlorobenzene, and HCl. Three molecules of the acid are produced for every molecule of lindane that reacts (Cremlyn, 1991 Kollig, 1993). [Pg.697]

Sethunathan, N. and Yoshida, T. Degradation of chlorinated hydrocarbons by Clostridiumsp. isolated from lindane-amended, flooded soil, Plant Soil 38 663-666, 1973a. [Pg.1722]

Chlorination of benzene gives an addition product that is a mixture of stereoisomers known collectively as hexachlorocyclohexane (HCH). At one time, this was incorrectly termed benzene hexachloride. The mixtnre has insecticidal activity, though activity was found to reside in only one isomer, the so-called gamma isomer, y-HCH. y-HCH, sometimes under its generic name lindane, has been a mainstay insecticide for many years, and is about the only example of the chlorinated hydrocarbons that has not been banned and is still available for general use. Although chlorinated hydrocarbons have proved very effective insecticides, they are not readily degraded in the environment, they accumulate and persist in animal tissues, and have proved toxic to many bird and animal species. [Pg.73]

The ARS Technologies, Inc., Ferox process is an in situ remediation technology for the treatment of chlorinated hydrocarbons, leachable heavy metals, and other contaminants. The process involves the subsurface injection and dispersion of reactive zero-valence iron powder into the saturated or unsaturated zones of a contaminated area. ARS Technologies claims that Ferox is applicable for treating the following chemicals trichloroethene (TCE), 1,1,1-trichloroethane (TCA), carbon tetrachloride, 1,1,2,2-tetrachloroethane, lindane, aromatic azo compounds, 1,2,3-trichloropropane, tetrachloroethene (PCE), nitro aromatic compounds, 1,2-dichloroethene (DCE), vinyl chloride, 4-chlorophenol, hexachloroethane, tribromomethane, ethylene dibromide (EDB), polychlorinated biphenyls (PCBs), Freon-113, unexploded ordinances (UXO), and soluble metals (copper, nickel, lead, cadmium, arsenic, and chromium). [Pg.377]

This technology is applicable for the treatment of polychlorinated biphenyls (PCBs) and other halogenated contaminants, such as insecticides, herbicides, pentachlorophenol (PCP), lindane, and chlorinated dibenzodioxins and furans. The contaminant matrix can be soil, sludge, sediments, or oil. It can treat oily sludges, coal by-products, and wood-treating compounds. [Pg.1079]

Lindane, the y-isomer of HCH, is a potent insecticide. Its insecticidal action is due to a hyperexcitatory effect on the insect s central nervous system induced by accumulation of acetylcholine in the synaptic region 73). We prepared a number of analogs in which some of the chlorine atoms are replaced by other substituents while maintaining the -configuration and determined their insecticidal activity against mosquitos74,). [Pg.149]

Figure 15.7 Structure of hexachlorocyclohexane (lindane) showing the axial and equatorial arrangement of the chlorine atoms in the active isomer. Figure 15.7 Structure of hexachlorocyclohexane (lindane) showing the axial and equatorial arrangement of the chlorine atoms in the active isomer.
Biocides most often found in the indoor environment are chlorinated hydrocarbons like chlordane, DDT, dieldrin, lindane, heptachlor and methoxychlor, pyrethroids like cyfluthrin, cypermethrin, and permethrin, organophosphates like chlorpyrifos, diazinon, dichlorvos, isofenfos, and malathion, carbamates like ben-diocarb, carbaryl and propoxur and chlorophenols like pentachlorophenol (PCP), chlorocresol (4-chloro-3-methylphenol) and o-phenylphenol. Residues formed in house dust may vary in different countries (Butte, 2003), but biocides like chlorpyrifos, DDT, methoxychlor, permethrin, pentchlorophenol and propoxur seem to be the active compounds in biocide formulations even in different continents, as they are found equally in house dust samples form Germany and the USA (Becker et al., 2002 Butte, 2003 Camann, Colt and Zuniga, 2002). Concentrations of biocides in house dust are mostly in the milligram per kilogram range, they seldom exceed a microgram per cubic meter in indoor air. [Pg.242]

Table 12.3 Dust concentrations of PCP, lindane, DDT and chlorinated naphthalenes in different locations of museums (reprinted from Schieweck et a ., 2007a with permission from Elsevier). Table 12.3 Dust concentrations of PCP, lindane, DDT and chlorinated naphthalenes in different locations of museums (reprinted from Schieweck et a ., 2007a with permission from Elsevier).
Lindane is a chlorinated pesticide with the following structure ... [Pg.196]

In the case of lindane, the lack of chlorinated intermediates indicate direct transformation to benzene. (Figure 5, Schiith and Reinhard 1998)... [Pg.54]

Toxaphene has been in use since 1949. It is a complex mixture that consists of at least 670 chlorinated terpenes (Jansson Wideqvist, 1983). It was used as a nonsystemic stomach and contact insecticide. As it is nontoxic to plants (except to cucurbius), it was used to control many insects that inhabited cotton, corn, fruit, vegetables and small grains, and to control the Cussia obtusifola soybean pest. Toxaphene solutions were usually mixed with other pesticides because it can help to solubilise other insecticides with lower water solubility (e.g. DDT, lindane, etc.) (ATSDR, 1996b). [Pg.396]

The American Public Health Association [97,98] published an early gas chromatographic method for the solvent extraction and gas chromatographic determination of 11 chlorinated insecticides in water samples in amounts, down to 0.005mg L 1 p,p -DT)E, p,p -DDT, Aldrin, Dieldrin, Endrin, Heptachlor, Heptachlor epoxide, Lindane, Isodrin and Methoxychlor. The insecticides Carbophenothion, Chlordane, Dioxathion, Diazinon, Ethion, Malathion, Parathion methyl, methyl Trithion, Parathion, Toxaphene and VC-13 may be determined when present at higher levels. Also, the chemicals chlordane, hexachlorobicycloheptadiene and hexachlorocyclopentadiene, which are pesticide manufacturing precursors, may be analysed by this method. [Pg.274]


See other pages where Chlorinated lindane is mentioned: [Pg.391]    [Pg.212]    [Pg.233]    [Pg.98]    [Pg.419]    [Pg.394]    [Pg.223]    [Pg.121]    [Pg.28]    [Pg.224]    [Pg.830]    [Pg.696]    [Pg.73]    [Pg.66]    [Pg.70]    [Pg.435]    [Pg.223]    [Pg.536]    [Pg.133]    [Pg.57]    [Pg.488]    [Pg.289]    [Pg.658]    [Pg.756]    [Pg.274]    [Pg.279]    [Pg.330]    [Pg.337]   
See also in sourсe #XX -- [ Pg.436 ]




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