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 f arenes together with the mineralization of chlorophenol.

5 studying electrochemical dechlorination of 2-chlorophenol (2-CP) in aqueous media, we find that cobal

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

7 ation of phenol, para- and ortho-substituted chlorophenols (2-Cl, 4-Cl, 2,4-diCl-, 2,6-diCl, and 2,4,

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

9 ity to simultaneously derivatize five CPs (2-chlorophenol, 2,4-dichlorophenol, 2,4,6-trichlorophenol,

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

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

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

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

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

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

16 Chlorophenol 4-monooxygenase activity responsible for 2,

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

18 With degradation of the pollutant 4-chlorophenol (4-CP) by Arthrobacter chlorophenolicus A6,

19 ethylene Blue (MB), Erythrosine B (ER) and 4-chlorophenol (4-CP) under sunlight irradiation.

20 chlorination and full mineralization of para-chlorophenol (4-CP), a toxic contaminant, are unfulfille

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

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

23 The oxidation rate constants of 4-chlorophenol, 4-tert-octylphenol, 4-bromophenol, and phe

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

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

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

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

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

29 Since chlorophenols are known to be precursors of polychlorina

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

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

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

33 sponses and higher specific responses toward chlorophenols compared to t-Bu(4)PcZn due to the electro

34 Zn-Hbimcp (Hbimcp = 2,6-bis((imino)methyl)-4-chlorophenol) coordination bond used in this work has a

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

36 five industrial and environmentally-relevant chlorophenols (CPs) employing trimethyloxonium tetrafluo

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

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

39 s, selenate reducers, and xylan, chitin, and chlorophenol degraders while KW strain was enriched with

40 dehalogenase gene, distantly related to the chlorophenol dehalogenase gene cprA (pairwise amino acid

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

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

43 These results suggest that chlorophenol exposure independent of phenoxyherbicides m

44 Chlorophenol exposure was assigned using both an intensi

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

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

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

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

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

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

51 0.26, p < 0.0001) but not levels of OH-PCBs, chlorophenols, or PFOS.

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

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

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

55 es with the concomitant degradation of toxic chlorophenol pollutants represents a new approach in env

56 aryl chlorides by chloro-group transfer from chlorophenol pollutants to arenes during their mineraliz

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

58 CPRG), which reacts with beta-gal to produce chlorophenol red (CPR) in a bacteria concentration-depen

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

60 he isolated bacteria are then incubated with chlorophenol red-beta-d-galactopyranoside (CPRG), which

61 The biosensor consists of the chlorophenol red-beta-D-galactopyranoside (CPRG)-loaded

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

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

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

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

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

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

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

69 5 and 7.5 for the p, p-dichlorophenol- and p-chlorophenol-substituted dyes, respectively).

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

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

72 notubes accelerates electron transfer from 4-chlorophenol to surface-bound peroxymonosulfate, increas

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

74 Levels of anilides, 2,6-dinitroanilines, chlorophenols, triclosan, and guanidines significantly i

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

76 droxydiphenylmethyl)pyrrolidin-1-ylmethyl]-4-chlorophenol) were prepared and three unknown complexes

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

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

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

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