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1 ribution shifting from 1,2-dichloroethane to trichloroethane.
2 uring growth with trichloromethane and 1,1,2-trichloroethane.
3                                        1,1,1-Trichloroethane (1,1,1-TCA) and trichloroethene (TCE) ar
4 es, such as carbon tetrachloride (CT); 1,1,1-trichloroethane (1,1,1-TCA); and 1,1-dichloroethane (1,1
5 waste from technical DDT [mainly 1,1'-(2,2,2-trichloroethane-1,1-diyl)bis(4-chlorobenzene), or 4,4'-D
6 (PCBs), 1,1-bis(4,4'-dichlorodiphenyl)-2,2,2-trichloroethane (4,4'-DDT), 1,1-bis(4,4'-dichlorodipheny
7 ticides--hexachlorobenzene, dichlorodiphenyl trichloroethane and its primary metabolite, dichlorodiph
8                               Chloroform and trichloroethanes are pervasive groundwater contaminants
9                 Global measurements of 1,1,1-trichloroethane (CH3CCl3, methyl chloroform) provide an
10 he insecticide 2,2-bis(p-chlorophenyl)-1,1,1-trichloroethane (DDT) and is a ubiquitous environmental
11 ding dieldrin, 1,1-bis(p-chlorophenyl)-2,2,2-trichloroethane (DDT), and pyrethroids.
12 s), hexachlorobenzene, p,p'-dichlorodiphenyl trichloroethane (DDT), o,p'-DDT, and p,p'-dichlorodiphen
13 species to the insecticide dichloro-diphenyl-trichloroethane (DDT).
14 1-dichloroethene, trichloroethene, and 1,1,1-trichloroethane) demonstrated that PRM was also more res
15  of early-life exposures to dichlorodiphenyl trichloroethane/dichlorodiphenyl dichloroethene and hexa
16  polychlorinated biphenyls, dichlorodiphenyl trichloroethane/dichlorodiphenyl dichloroethene and hexa
17  polychlorinated biphenyls, dichlorodiphenyl trichloroethane/dichlorodiphenyl dichloroethene or hexac
18 henol AF, and 2-2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (group 1) strongly activated ERalpha est
19 r metabolite 2,2-bis(p-hydroxyphenyl)-1,1, 1-trichloroethane (HPTE) with estrogen receptor alpha (ERa
20               DDT (bis[4-chlorophenyl]-1,1,1-trichloroethane) is a persistent insecticide that was us
21  1-(o-chlorophenyl)-1-(p-chlorophenyl)-2,2,2-trichloroethane (o,p'-DDT) and beta-hexachlorocyclohexan
22                           Replacement of the trichloroethane or dichloroethylene group with a methyl
23 ntly affected by cocontaminants (i.e., 1,1,1-trichloroethane or trichloroethylene), but were slowed b
24 ntaminants such as bis[4-chlorophenyl]-1,1,1-trichloroethane (p,p'-DDT) or its metabolites, such as b
25 es in emissions of methyl chloroform (1,1, 1-trichloroethane) resulting from the Montreal Protocol pr
26 fe = 31 months; n = 34) was lower than 1,1,1-trichloroethane (TCA) but similar to 1,1-dichloroethene
27                                        1,1,1-Trichloroethane (TCA) is a ubiquitous environmental poll
28 een their activity on chloroform (CF), 1,1,1-trichloroethane (TCA), and 1,1,2-TCA.
29 ater co-contaminated with 1,4-dioxane, 1,1,1-trichloroethane (TCA), and trichloroethene (TCE) is amon
30 thene (cDCE) > trichloroethene (TCE) > 1,1,1-trichloroethane (TCA).
31  the commonly abused solvents toluene, 1,1,1-trichloroethane (TCE), and trichloroethylene (TCY) affec
32 isposal of industrial DDT (dichloro-diphenyl-trichloroethane) waste off Southern California is implic