ライフサイエンスコーパス: chlorophenol

1 ic NO conversion and in the degradation of 4-chlorophenol.

2 nol while dibenzo-p-dioxin was formed from o-chlorophenol.

3 no-m-cresol, 2-amino-m-cresol, and 2-amino-4-chlorophenol.

4 The electrochemical degradation of 2-chlorophenol (2-CP) on boron-doped diamond (BDD) anodes

5 d phenols (2-chlorophenol, 3-chlorophenol, 4-chlorophenol, 2,4-dichlorophenol, 2,4,6-trichlorophenol,

6 emerging (2,4,5 trichlorophenol, 2-benzyl-4-chlorophenol, 2-chloro-4-phenylphenol, and bis(5-chloro-

7 posed to different dosages of tetradecane, 4-chlorophenol, 2-chlorobiphenyl, naphthalene, benzene, me

8 f certain organic compounds (e.g., phenol, 4-chlorophenol, 2-chlorophenol, salicylic acid, catechol,

9 xcited o-phenylene thioxocarbonate (2) and 2-chlorophenol (3) efficiently form the carbene species wh

10 (1), o-phenylene thioxocarbonate (2), and 2-chlorophenol (3) in solution was studied using time-reso

11 The analysis of chlorinated phenols (2-chlorophenol, 3-chlorophenol, 4-chlorophenol, 2,4-dichlo

12 Chlorophenol 4-monooxygenase activity responsible for 2,

13 Chlorophenol 4-monooxygenase is a key enzyme in the degr

14 The representative wastewater pollutant, 4-chlorophenol (4-CP), is readily oxidized (ultimately to

15 is of chlorinated phenols (2-chlorophenol, 3-chlorophenol, 4-chlorophenol, 2,4-dichlorophenol, 2,4,6-

16 With 4-chlorophenol, a dimerized product is formed, consistent

17 d led to the formation of a 9:1 mixture of 2-chlorophenol and 3-chlorophenol, via a mechanism involvi

18 xylene (BTEX) and polar compounds, phenol, 4-chlorophenol and 4-nitrophenol are extracted under heads

19 loro-6-hydroxy-cyclohexa-2-ene-1,4-dione via chlorophenol and chlorobenzoquinone intermediates.

20 As all chlorophenols are degraded by micro-organisms, novel bio

21 Since chlorophenols are known to be precursors of polychlorina

22 aces catalyze the generation of PCDD/Fs from chlorophenols at the upper range of the catalytic format

23 ichlorobenzenes and trichlorobenzenes to the chlorophenols, but no products were detected for the hea

24 ctions was exploited to extract carcinogenic chlorophenols (CCPs) from environmental waters, and a si

25 spectively, and dechlorinated 2,3,6-TCP to 3-chlorophenol (CP) via 2,5-DCP.

26 The accumulation of chlorophenols (CPs) in the environment, due to their wid

27 However, Pt(4+) changed the 2-chlorophenol degradation rate only slightly, and Fe(3+)

28 metal-free photochemical reaction between 2-chlorophenol derivatives and terminal alkynes by tandem

29 y associated with ever having high-intensity chlorophenol exposure (odds ratio = 1.79, 95% confidence

30 These results suggest that chlorophenol exposure independent of phenoxyherbicides m

31 Chlorophenol exposure was assigned using both an intensi

32 To evaluate the association of chlorophenol exposure with soft tissue sarcoma risk inde

33 vents spontaneously form an organogel when p-chlorophenol is added in a 1:1 AOT:phenol molar ratio.

34 Furthermore, reaction of DHP with 4-chlorophenol leads to a dimeric product.

35 n of halorespiratory genes upon binding of o-chlorophenol ligands and is reversibly inactivated by ox

36 nd tryptophan) and environmental pollutants (chlorophenol mixtures).

37 contribution studies partial oxidation of 2-chlorophenol on surfaces of neat silica at temperatures

38 0.26, p < 0.0001) but not levels of OH-PCBs, chlorophenols, or PFOS.

39 yellow enzyme (OYE) and OYE complexed with p-chlorophenol (p-Cl phenol).

40 orobenzoic acid, 3,5-difluorobenzoic acid, 2-chlorophenol, p-tert-butylphenol, and dimethyl sulfoxide

41 tion (ABD), (ii) use and production of penta-chlorophenol (PCP), (iii) use and production of tetra-ch

42 The mild conditions and the application to chlorophenols rather of the more expensive bromo or iodo

43 plex, we performed a colorimetric assay with chlorophenol red-beta-d-galactopyranoside (CPRG) for bac

44 ) the release of beta-gal was detected using chlorophenol red-beta-d-galactopyranoside (CRPG), a colo

45 c acid and three substrates, a colorimetric (chlorophenol red-beta-D-galactopyranoside), a chemilumin

46 mon pH-indicator dyes, bromophenol blue, and chlorophenol red.

47 e within the Desulfitobacterium dehalogenans chlorophenol reductase (cpr) gene cluster (cprK) was pro

48 comparable to toxicity sequences of various chlorophenols reported in the literature.

49 c compounds (e.g., phenol, 4-chlorophenol, 2-chlorophenol, salicylic acid, catechol, maleic acid, oxa

50 chlorinated phenols and chemicals containing chlorophenol side-chains such as triclosan.

51 nol (PCP), (iii) use and production of tetra-chlorophenol (TeCP), (iv) high temperature processes (Th

52 In addition to chlorophenols, the enzyme also hydroxylated some chloro-

53 model, the toxicity differences among seven chlorophenols to E. faecalis and fresh mixed anaerobic s

54 ion of a 9:1 mixture of 2-chlorophenol and 3-chlorophenol, via a mechanism involving O-O homolytic cl

55 i.e., chlorodiphenyl ether was formed from p-chlorophenol while dibenzo-p-dioxin was formed from o-ch

56 tivity were revealed by the degradation of 2-chlorophenols with an UV light source.

57 atalyzed the hydroxylation of several tested chlorophenols with the coconsumption of NADH and oxygen.

58 Blood samples collected from 56 former chlorophenol workers in 2004-2005 and again in 2010 were