ライフサイエンスコーパス: pentachlorophenol

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1 ching of bSULT1A1 fluorescence observed with pentachlorophenol.

2 nd hexachlorobenzene were oxidized slowly to pentachlorophenol.

3 ganism capable of complete mineralization of pentachlorophenol.

4 induced in S. chlorophenolica in response to pentachlorophenol.

5 , 2,4-dichlorophenol, 2,4,5-trichlorophenol, pentachlorophenol, 4-nitrobenzyl-chloride, 2,4-dichloroa

6 orophenolica, a soil bacterium that degrades pentachlorophenol, a widely used wood preservative.

7 Pentachlorophenol and other chlorinated phenols are high

8 ldlife tissues, including OH-PCBs, OH-PBDEs, Pentachlorophenol, and polybromophenols.

9 islation (e.g., maximum permitted levels for pentachlorophenol are in the range 0.4-1 mug.L(-1)).

10 chlorohydroquinone during the degradation of pentachlorophenol by Sphingbium chlorophenolicum.

11 ,6-dichlorohydroquinone in the catabolism of pentachlorophenol by Sphingobium chlorophenolicum ATCC 3

12 The initial step in the degradation of pentachlorophenol by Sphingobium chlorophenolicum genera

13 6-dichlorohydroquinone during degradation of pentachlorophenol by Sphingobium chlorophenolicum.

14 droquinone in the pathway for degradation of pentachlorophenol by Sphingobium chlorophenolicum.

15 he biodegradation of the xenobiotic compound pentachlorophenol by Sphingobium chlorophenolicum.

16 hydrogen atoms during the biodegradation of pentachlorophenol by Sphingomonas chlorophenolica.

17 Finally, titrations of bSULT1A1-pentachlorophenol complex with palmitoyl-CoA caused the

18 contaminated soil from the United States and pentachlorophenol from a certified reference material (C

19 In the presence of PcpD, TCBQ formed by pentachlorophenol hydroxylase (PcpB) is sequestered unti

20 reactions in the pathway for degradation of pentachlorophenol in the soil bacterium Sphingobium chlo

21 , 2,4-dichlorophenol, 2,4,6-trichlorophenol, pentachlorophenol) in river water was accomplished using

22 atalysts, to destroy the priority pollutants pentachlorophenol (PCP) and 2,4,6-trichlorophenol (TCP).

23 transferase and acetyltransferase inhibitors pentachlorophenol (PCP) and 2,6-dichloro-4-nitrophenol (

24 perfund wood-treating site contaminated with pentachlorophenol (PCP) and the environmentally persiste

25 The biochemistry of pentachlorophenol (PCP) degradation by Flavobacterium sp

26 The first step in the pentachlorophenol (PCP) degradation pathway in Sphingobi

27 The first three enzymes of the pentachlorophenol (PCP) degradation pathway in Sphingobi

28 Pentachlorophenol (PCP) is a toxic pollutant.

29 Pentachlorophenol (PCP) is globally dispersed and contam

30 The effect of extracellularly applied pentachlorophenol (PCP) was studied on the membrane pote

31 oethene (4,4'-DDE), hexachlorobenzene (HCB), pentachlorophenol (PCP)).

32 from soil that was heavily contaminated with pentachlorophenol (PCP), a toxic pesticide introduced in

33 ites of polychlorinated biphenyls (OH-PCBs), pentachlorophenol (PCP), and perfluorooctane sulfonate (

34 produced not by the most-highly chlorinated pentachlorophenol (PCP), but rather by the less chlorina

35 nd their hydroxylated metabolites (HO-PCBs), pentachlorophenol (PCP), polybrominated diphenyl ethers,

36 c sludge, with or without 10 mg L(-1) spiked pentachlorophenol (PCP), we found it was clear that the

37 The quinone site inhibitor pentachlorophenol perturbs the heme optical spectrum of

38 nsforming phenolic organic compounds such as pentachlorophenol, phenolic acids, and triclosan via sur

39 enoxide at pH 8.3, midway between the pKa of pentachlorophenol (pKa = 4.8) and that of hydrogen perox

40 n, forchlorfenuron, imidacloprid, malathion, pentachlorophenol, pyraclostrobin, sulfasalazine, and tr

41 tyi strain JNA in pure culture dechlorinated pentachlorophenol to 3,5-dichlorophenol (DCP) via remova

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