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1 es, such as carbon tetrachloride (CT); 1,1,1-trichloroethane (1,1,1-TCA); and 1,1-dichloroethane (1,1
2 (PCBs), 1,1-bis(4,4'-dichlorodiphenyl)-2,2,2-trichloroethane (4,4'-DDT), 1,1-bis(4,4'-dichlorodipheny
3 ticides--hexachlorobenzene, dichlorodiphenyl trichloroethane and its primary metabolite, dichlorodiph
5 he insecticide 2,2-bis(p-chlorophenyl)-1,1,1-trichloroethane (DDT) and is a ubiquitous environmental
7 s), hexachlorobenzene, p,p'-dichlorodiphenyl trichloroethane (DDT), o,p'-DDT, and p,p'-dichlorodiphen
9 of early-life exposures to dichlorodiphenyl trichloroethane/dichlorodiphenyl dichloroethene and hexa
10 polychlorinated biphenyls, dichlorodiphenyl trichloroethane/dichlorodiphenyl dichloroethene and hexa
11 polychlorinated biphenyls, dichlorodiphenyl trichloroethane/dichlorodiphenyl dichloroethene or hexac
12 henol AF, and 2-2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (group 1) strongly activated ERalpha est
13 r metabolite 2,2-bis(p-hydroxyphenyl)-1,1, 1-trichloroethane (HPTE) with estrogen receptor alpha (ERa
15 1-(o-chlorophenyl)-1-(p-chlorophenyl)-2,2,2-trichloroethane (o,p'-DDT) and beta-hexachlorocyclohexan
17 ntaminants such as bis[4-chlorophenyl]-1,1,1-trichloroethane (p,p'-DDT) or its metabolites, such as b
18 es in emissions of methyl chloroform (1,1, 1-trichloroethane) resulting from the Montreal Protocol pr
19 fe = 31 months; n = 34) was lower than 1,1,1-trichloroethane (TCA) but similar to 1,1-dichloroethene
22 the commonly abused solvents toluene, 1,1,1-trichloroethane (TCE), and trichloroethylene (TCY) affec
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