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1 anerochaete chrysosporium mineralizes 2,4, 6-trichlorophenol.
2 intermediate of 2,4,5-T degradation is 2,4,5-trichlorophenol.
3 benzyl-4-chorophenol, and 50.6 muM for 2,4,5-trichlorophenol.
7 HP A has most often been studied using 2,4,6-trichlorophenol (2,4,6-TCP) as a substrate analogue beca
8 r mixture predominantly to tetra-BDEs, 2,4,6-trichlorophenol (2,4,6-TCP) to 4-CP, and tetrachloroethe
11 h), 2,4-dichlorophenol (2,4-DCPh), and 2,4,6-trichlorophenol (2,4,6-TriCPh), but have detected no chl
12 n and triclocarban) and four emerging (2,4,5 trichlorophenol, 2-benzyl-4-chlorophenol, 2-chloro-4-phe
13 ,4-dichlorophenol; 2,5-dichlorophenol; 2,4,5-trichlorophenol; 2,4,6-trichlorophenol; benzophenone-3 (
14 sidered to be the native substrate and 2,4,6-trichlorophenol also gives high turnover rates in enzyma
15 med DHP Compound ES with the substrate 2,4,6-trichlorophenol and demonstrate the catalytic competency
16 (gemfibrozil, nonylphenol, triclosan, 2,4,6-trichlorophenol, and naphthenic acids), with detection l
17 strates 2,4,6-tribromophenol (TBP) and 2,4,6-trichlorophenol are oxidatively dehalogenated by DHP to
18 e highly active in conjugating DCA and 2,4,5-trichlorophenol, as well as several other chlorinated ph
19 dichlorophenol; 2,4,5-trichlorophenol; 2,4,6-trichlorophenol; benzophenone-3 (2-hydroxy-4-metoxybenzo
20 sotopic fractionation during oxidative 2,4,6-trichlorophenol dechlorination by representative soil en
21 monooxygenase activity responsible for 2,4,5-trichlorophenol degradation was detected in the cell ext
22 ociation constant of 2-nitrophenol and 2,4,6-trichlorophenol from ITP experiments with fluorescent ca
23 The pathway for the degradation of 2,4, 6-trichlorophenol has been elucidated by the characterizat
25 of chemical toxins (2-nitrophenol and 2,4,6-trichlorophenol) in tap water, with no sample preparatio
26 ria cepacia AC1100 completely degrades 2,4,5-trichlorophenol, in which an FADH(2)-dependent monooxyge
27 to 5-chlorohydroxyquinol but converted 2,4,6-trichlorophenol only to 2,6-dichloro-p-quinol as the fin
28 l, 4-chlorophenol, 2,4-dichlorophenol, 2,4,6-trichlorophenol, pentachlorophenol) in river water was a
29 bofuran, carbaryl, 2,4-dichlorophenol, 2,4,5-trichlorophenol, pentachlorophenol, 4-nitrobenzyl-chlori
30 e, chlorobenzene, 1,2-dichlorobenzene, 2,4,6-trichlorophenol, pentafluorophenol, and nitrobenzene.
31 imes the amount of 2,4 dichlorophenol, 2,4,6 trichlorophenol, phorate D10, fonofos, chloropyrifos, an
33 examined 1,615 workers exposed to dioxins in trichlorophenol production in Midland, Michigan, to dete
34 orinated 2,3,4,6-tetrachlorophenol via 2,4,6-trichlorophenol (TCP) and 2,4,5-TCP to 2,4-DCP and 3,4-D
35 bination of H(2)O(2) and the substrate 2,4,6-trichlorophenol (TCP) brings about facile switching of o
41 enzyme was responsible for converting 2,4,5-trichlorophenol to 2,5-dichloro-p-hydroquinone and then
43 taining a model organic contaminant, such as trichlorophenol, with glucose in oxygen-saturated water
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