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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 , 2,4-dichlorophenol, 2,4,6-trichlorophenol, pentachlorophenol and triclosan) in six distinct, separa
9 ldlife tissues, including OH-PCBs, OH-PBDEs, Pentachlorophenol, and polybromophenols.
10 islation (e.g., maximum permitted levels for pentachlorophenol are in the range 0.4-1 mug.L(-1)).
11 chlorohydroquinone during the degradation of pentachlorophenol by Sphingbium chlorophenolicum.
12 ,6-dichlorohydroquinone in the catabolism of pentachlorophenol by Sphingobium chlorophenolicum ATCC 3
13       The initial step in the degradation of pentachlorophenol by Sphingobium chlorophenolicum genera
14 6-dichlorohydroquinone during degradation of pentachlorophenol by Sphingobium chlorophenolicum.
15 droquinone in the pathway for degradation of pentachlorophenol by Sphingobium chlorophenolicum.
16 he biodegradation of the xenobiotic compound pentachlorophenol by Sphingobium chlorophenolicum.
17  hydrogen atoms during the biodegradation of pentachlorophenol by Sphingomonas chlorophenolica.
18              Finally, titrations of bSULT1A1-pentachlorophenol complex with palmitoyl-CoA caused the
19  between pollutants and hormone ratios, with pentachlorophenol, dimethylthiophosphate, 3-phenoxybenzo
20 methoxychlor, lindane, tributyltin chloride, pentachlorophenol, diuron, and ethofumesate.
21  N-acylsaccharins, pentafluorophenol esters, pentachlorophenol esters, N-hydroxybenzotriazole esters,
22 contaminated soil from the United States and pentachlorophenol from a certified reference material (C
23      In the presence of PcpD, TCBQ formed by pentachlorophenol hydroxylase (PcpB) is sequestered unti
24  reactions in the pathway for degradation of pentachlorophenol in the soil bacterium Sphingobium chlo
25 , 2,4-dichlorophenol, 2,4,6-trichlorophenol, pentachlorophenol) in river water was accomplished using
26 atalysts, to destroy the priority pollutants pentachlorophenol (PCP) and 2,4,6-trichlorophenol (TCP).
27 transferase and acetyltransferase inhibitors pentachlorophenol (PCP) and 2,6-dichloro-4-nitrophenol (
28 perfund wood-treating site contaminated with pentachlorophenol (PCP) and the environmentally persiste
29                          The biochemistry of pentachlorophenol (PCP) degradation by Flavobacterium sp
30                        The first step in the pentachlorophenol (PCP) degradation pathway in Sphingobi
31               The first three enzymes of the pentachlorophenol (PCP) degradation pathway in Sphingobi
32                                              Pentachlorophenol (PCP) is a toxic pollutant.
33                                              Pentachlorophenol (PCP) is globally dispersed and contam
34        The effect of extracellularly applied pentachlorophenol (PCP) was studied on the membrane pote
35 oethene (4,4'-DDE), hexachlorobenzene (HCB), pentachlorophenol (PCP)).
36 from soil that was heavily contaminated with pentachlorophenol (PCP), a toxic pesticide introduced in
37 ites of polychlorinated biphenyls (OH-PCBs), pentachlorophenol (PCP), and perfluorooctane sulfonate (
38  produced not by the most-highly chlorinated pentachlorophenol (PCP), but rather by the less chlorina
39 u(bpy)2(dppz)]Cl2 was remarkably enhanced by pentachlorophenol (PCP), by forming ion-pairing complexe
40 nd their hydroxylated metabolites (HO-PCBs), pentachlorophenol (PCP), polybrominated diphenyl ethers,
41 c sludge, with or without 10 mg L(-1) spiked pentachlorophenol (PCP), we found it was clear that the
42 e production in paddy soil contaminated with pentachlorophenol (PCP).
43                   The quinone site inhibitor pentachlorophenol perturbs the heme optical spectrum of
44 nsforming phenolic organic compounds such as pentachlorophenol, phenolic acids, and triclosan via sur
45 enoxide at pH 8.3, midway between the pKa of pentachlorophenol (pKa = 4.8) and that of hydrogen perox
46 n, forchlorfenuron, imidacloprid, malathion, pentachlorophenol, pyraclostrobin, sulfasalazine, and tr
47 tyi strain JNA in pure culture dechlorinated pentachlorophenol to 3,5-dichlorophenol (DCP) via remova