ライフサイエンスコーパス: chlorobenzene

1 f 3 with HCl or by direct photolysis of 2 in chlorobenzene.

2 thanogenic culture would completely detoxify chlorobenzene.

3 ulation of benzene, which is more toxic than chlorobenzene.

4 constants were similar in toluene, THF, and chlorobenzene.

5 C=C(t)Bu))(2)][B(C(6)F(5))(4)](2).5PhCl from chlorobenzene.

6 N-bromosuccinimide) and 5 mol % Pd(OAc)2 in chlorobenzene (0.10 molar) at 110 degrees C, pyridine-di

7 for aniline, phenol, benzene, bromobenzene, chlorobenzene, 1,2-dichlorobenzene, 2,4,6-trichloropheno

8 nt sources of chlorobenzene and a mixture of chlorobenzene, 1,2-dichlorobenzene, and 1,4-dichlorobenz

9 o the strain the ability to oxidize toluene, chlorobenzene, 3,4-dichloro-1-butene, and indole.

10 : no guest, 611; toluene, 565; benzene, 586; chlorobenzene, 592; p-xylene, 585; mesitylene, 565; etha

11 ; and incubation of cells with 2,4-dinitro-1-chlorobenzene (an inhibitor of thioredoxin reductase) de

12 s, with a kinh of 6.1 x 10(4) M(-1) s(-1) in chlorobenzene and 6.0 x 10(3) M(-1) s(-1) in acetonitril

13 y column studies with contaminant sources of chlorobenzene and a mixture of chlorobenzene, 1,2-dichlo

14 d by shifts in the carbon isotopic ratios of chlorobenzene and benzene during degradation.

15 Sustainable degradation of chlorobenzene and benzene was observed in the microcosms

16 er solid-liquid phase-transfer conditions in chlorobenzene and in the presence of K(3)PO(4) as weak b

17 13)C measure of salmon density, but mercury, chlorobenzenes, and polychlorinated biphenyls (PCBs) wer

18 s were obtained with analytes as volatile as chlorobenzene (approximately 90%) in 1 mL of solvent.

19 4c crystallizes from chlorobenzene as 4c(ClPh).0.5PhCl, which has been charac

20 tion limits on column for all analytes using chlorobenzene as a dopant.

21 4), CHCl(3), CH(2)Cl(2), dichloroethane, and chlorobenzene at -23 degrees C showed little variance.

22 pronounced solvent effect is observed: While chlorobenzene causes the T2 planes to align preferential

23 ies showed that a small percentage of ODT in chlorobenzene (CB) induced the nucleation of polymeric c

24 sites contaminated with nitrobenzene (NB) or chlorobenzene (CB) were tested for their biodegradation

25 the vadose zone of a site contaminated with chlorobenzene (CB), 1,2-dichlorobenzene (12DCB), and 1,4

26 of PTB7 film formation from chloroform (CF), chlorobenzene (CB), and 1,2-dichlorobenzene (DCB) soluti

27 ltrichloroethane and its metabolites (DDTs), chlorobenzenes (CBzs)--pentachlorobenzene and hexachloro

28 to evaluate an online monitoring system for chlorobenzene congeners as indicators of polychlorinated

29 Isolation of specific chlorobenzene congeners from other same-mass compounds w

30 Continuous measurements of chlorobenzene congeners using gas chromatography coupled

31 p-xylene and the incoming arene is C(6)D(6), chlorobenzene-d(5), anisole-d(8), fluorobenzene-d(5), to

32 rocarbons (mixture of chlorobenzene-h(5) and chlorobenzene-d(5), mixture of 1,2-dichlorobenzene-h(4)

33 To this end, active chlorobenzene-dechlorinating microcosms that were produc

34 d show that benzene derived electrons fueled chlorobenzene dechlorination removing the need to provid

35 of certain HiPco SWNTs upon reaction with 4-chlorobenzene diazonium and 4-hydroxybenzene diazonium s

36 toluminescence (PL) during a reaction with 4-chlorobenzene diazonium in aqueous solution, evidence fo

37 including aromatic hydrocarbons (mixture of chlorobenzene-h(5) and chlorobenzene-d(5), mixture of 1,

38 here 5x10(8)cells/ml degraded 125 nmol/ml of chlorobenzene in 150 min.

39 inated the overall partitioning of the three chlorobenzenes in the 1.5 mum filtrate, and the partitio

40 rmediate biodegradation products benzene and chlorobenzene increased and achieved steady state values

41 Chlorobenzene is a widespread groundwater contaminant fo

42 on acceptors tested, and dehalogenated every chlorobenzene isomer except 1,4-DCB.

43 and honokiol trapped two peroxyl radicals in chlorobenzene (kinh = 3.8 x 10(4) M(-1) s(-1)) and four

44 d catalytic amounts of pyridine in refluxing chlorobenzene leads to the formation of acyl chlorides.

45 he nanostructures in the droplet-based water-chlorobenzene MEs were in the range of 1 to 11 nm.

46 iate chlorine atoms from individual oriented chlorobenzene molecules adsorbed on a Si(111)-7 x 7 surf

47 he use of silver, previously unexplored, and chlorobenzene-normally regarded as relatively inert in s

48 orption and reactions of phenylacetylene and chlorobenzene on Ag(100).

49 is shows that p-SIDT(FBTTh2)2 spin-cast from chlorobenzene organizes into crystalline domains with la

50 her industrial or byproduct organochlorines (chlorobenzenes, pentachloroanisole, octachlorostyrene),

51 In refluxing chlorobenzene pure 1b was converted to the more thermody

52 Reductive dechlorination of chlorobenzene requires input of electron donor and resul

53 tical lamotrigine and the industrial solvent chlorobenzene, signifying that electrocatalytic treatmen

54 romonomers 16 in the presence of end-capping chlorobenzene solvent to produce the statistical spacerl

55 Enumeration of bacteria capable of degrading chlorobenzenes suggested that most of the biodegradation

56 lion (3-[2,4 dihydroxyphenylazo]-2-hydroxy-5-chlorobenzene sulfonic acid), the DNA stain 4',6-diamino

57 ylbenzene, carbon tetrachloride, chloroform, chlorobenzene, tetrachlorethane, and dichlorobenzene.

58 lture capable of reductive dechlorination of chlorobenzene to benzene with a second benzene-degrading

59 ing from simple aromatics (e.g., aniline and chlorobenzene) to the much larger squalene (M(w) = 411)

60 efficiently than alpha-tocopherol in a water/chlorobenzene two-phase system containing N-acetylcystei

61 ombination resulted in the transformation of chlorobenzene via benzene to the nontoxic degradation pr

62 The dispersions were composed of water-chlorobenzene (water analysis) and water-oleic acid (mon

63 more efficiently than alpha-tocopherol in a chlorobenzene/water two-phase system.

64 Benzene and chlorobenzene were treated aerobically on site in an exi

65 ch 1,2-dithienyl-1,2-dicyanoethene (4TCE) in chlorobenzene with ultrafast transient absorption spectr

66 alogenation capability of each strain to use chlorobenzenes with three or more chlorines, tetrachloro

67 Spincasting GRIM POPT from chlorobenzene yields a thin film with a 1.8 eV band gap,