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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.
4                                        2,4,6-Trichlorophenol (2) and 2,4,6-trichloro-m-cresol (5) rea
5                          TftD oxidizes 2,4,5-trichlorophenol (2,4,5-TCP) to 2,5-dichloro-p-benzoquino
6              Ralstonia eutropha JMP134 2,4,6-trichlorophenol (2,4,6-TCP) 4-monooxygenase catalyzes se
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
9 P134 is involved in the degradation of 2,4,6-trichlorophenol (2,4,6-TCP), a toxic pollutant.
10 cluding 2,4-dichlorophenoxyacetate and 2,4,6-trichlorophenol (2,4,6-TCP).
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 h 2,4-dichlororesorcinol (bpeD.dcr) or 2,4,6-trichlorophenol (bpeD.tcp) formed by supramolecular temp
21 sotopic fractionation during oxidative 2,4,6-trichlorophenol dechlorination by representative soil en
22 monooxygenase activity responsible for 2,4,5-trichlorophenol degradation was detected in the cell ext
23 ociation constant of 2-nitrophenol and 2,4,6-trichlorophenol from ITP experiments with fluorescent ca
24    The pathway for the degradation of 2,4, 6-trichlorophenol has been elucidated by the characterizat
25 case activity and the enhanced resistance to trichlorophenol in soils.
26  of chemical toxins (2-nitrophenol and 2,4,6-trichlorophenol) in tap water, with no sample preparatio
27 ria cepacia AC1100 completely degrades 2,4,5-trichlorophenol, in which an FADH(2)-dependent monooxyge
28                                              Trichlorophenol is readily oxidized to chloromaleic acid
29 to 5-chlorohydroxyquinol but converted 2,4,6-trichlorophenol only to 2,6-dichloro-p-quinol as the fin
30 s (2-chlorophenol, 2,4-dichlorophenol, 2,4,6-trichlorophenol, pentachlorophenol and triclosan) in six
31 l, 4-chlorophenol, 2,4-dichlorophenol, 2,4,6-trichlorophenol, pentachlorophenol) in river water was a
32 bofuran, carbaryl, 2,4-dichlorophenol, 2,4,5-trichlorophenol, pentachlorophenol, 4-nitrobenzyl-chlori
33 e, chlorobenzene, 1,2-dichlorobenzene, 2,4,6-trichlorophenol, pentafluorophenol, and nitrobenzene.
34 imes the amount of 2,4 dichlorophenol, 2,4,6 trichlorophenol, phorate D10, fonofos, chloropyrifos, an
35                                   In 1976, a trichlorophenol plant exploded in Seveso, Italy.
36 examined 1,615 workers exposed to dioxins in trichlorophenol production in Midland, Michigan, to dete
37 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
38 bination of H(2)O(2) and the substrate 2,4,6-trichlorophenol (TCP) brings about facile switching of o
39                          Specifically, 2,4,6-trichlorophenol (TCP) is converted to 2,6-dichloro-1,4-b
40 uding three tetrachlorophenol (TeCP) and six trichlorophenol (TCP) isomers.
41                Reaction of CCPO-I with 2,4,6-trichlorophenol (TCP) quickly yielded CCPO-II.
42 llutants 3,4-dichloroaniline (DCA) and 2,4,5-trichlorophenol (TCP).
43 pollutants pentachlorophenol (PCP) and 2,4,6-trichlorophenol (TCP).
44 e (H(2)O(2)) before organic substrate [2,4,6-trichlorophenol (TCP)] is demonstrated.
45 olite diethyl-phosphate (DEP); and (2) 2,4,6-trichlorophenol (TCP-246) and DEP.
46  enzyme was responsible for converting 2,4,5-trichlorophenol to 2,5-dichloro-p-hydroquinone and then
47                           It converted 2,4,5-trichlorophenol to 2,5-dichloro-p-quinol and then to 5-c
48 taining a model organic contaminant, such as trichlorophenol, with glucose in oxygen-saturated water