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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 : toluene, ethyl acetate, diethyl ether, and chlorobenzene.
7  N-bromosuccinimide) and 5 mol % Pd(OAc)2 in chlorobenzene (0.10 molar) at 110 degrees C, pyridine-di
8  for aniline, phenol, benzene, bromobenzene, chlorobenzene, 1,2-dichlorobenzene, 2,4,6-trichloropheno
9 nt sources of chlorobenzene and a mixture of chlorobenzene, 1,2-dichlorobenzene, and 1,4-dichlorobenz
10 o the strain the ability to oxidize toluene, chlorobenzene, 3,4-dichloro-1-butene, and indole.
11  4.8 x 10(5) M(-1)s(-1) for PMHC and CAPE in chlorobenzene (30 C).
12  4.8 x 10(5) M(-1)s(-1) for PMHC and CAPE in chlorobenzene (30 degrees C).
13 : no guest, 611; toluene, 565; benzene, 586; chlorobenzene, 592; p-xylene, 585; mesitylene, 565; etha
14 ; and incubation of cells with 2,4-dinitro-1-chlorobenzene (an inhibitor of thioredoxin reductase) de
15 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
16 y column studies with contaminant sources of chlorobenzene and a mixture of chlorobenzene, 1,2-dichlo
17 d by shifts in the carbon isotopic ratios of chlorobenzene and benzene during degradation.
18                   Sustainable degradation of chlorobenzene and benzene was observed in the microcosms
19 er solid-liquid phase-transfer conditions in chlorobenzene and in the presence of K(3)PO(4) as weak b
20 ifferent solvents (toluene, dichloromethane, chlorobenzene, and benzyl alcohol).
21 rcalated moderately polar solvents o-xylene, chlorobenzene, and o-dichlorobenzene show evidence of ch
22 13)C measure of salmon density, but mercury, chlorobenzenes, and polychlorinated biphenyls (PCBs) wer
23 es to highlight key roles of Dehalobacter as chlorobenzene- and HCH -respiring bacteria and demonstra
24 s were obtained with analytes as volatile as chlorobenzene (approximately 90%) in 1 mL of solvent.
25 es such as benzene, toluene, and deactivated chlorobenzene are phosphorylated in quantitative yields.
26                                              Chlorobenzenes are common soil contaminants in rural are
27                         4c crystallizes from chlorobenzene as 4c(ClPh).0.5PhCl, which has been charac
28 heric-pressure photoionization (dAPPI) using chlorobenzene as a dopant generates radical cations (M(+
29 tion limits on column for all analytes using chlorobenzene as a dopant.
30 as a dopant, and radical cations produced by chlorobenzene-assisted muLC-APPI with post-column additi
31 4), CHCl(3), CH(2)Cl(2), dichloroethane, and chlorobenzene at -23 degrees C showed little variance.
32 pronounced solvent effect is observed: While chlorobenzene causes the T2 planes to align preferential
33 ies showed that a small percentage of ODT in chlorobenzene (CB) induced the nucleation of polymeric c
34 sites contaminated with nitrobenzene (NB) or chlorobenzene (CB) were tested for their biodegradation
35  the vadose zone of a site contaminated with chlorobenzene (CB), 1,2-dichlorobenzene (12DCB), and 1,4
36 of PTB7 film formation from chloroform (CF), chlorobenzene (CB), and 1,2-dichlorobenzene (DCB) soluti
37  efficient sorbent, was developed to extract chlorobenzenes (CBs) from paddy soil, agricultural waste
38 ltrichloroethane and its metabolites (DDTs), chlorobenzenes (CBzs)--pentachlorobenzene and hexachloro
39  to evaluate an online monitoring system for chlorobenzene congeners as indicators of polychlorinated
40                        Isolation of specific chlorobenzene congeners from other same-mass compounds w
41                   Continuous measurements of chlorobenzene congeners using gas chromatography coupled
42 p-xylene and the incoming arene is C(6)D(6), chlorobenzene-d(5), anisole-d(8), fluorobenzene-d(5), to
43 rocarbons (mixture of chlorobenzene-h(5) and chlorobenzene-d(5), mixture of 1,2-dichlorobenzene-h(4)
44                          To this end, active chlorobenzene-dechlorinating microcosms that were produc
45 d show that benzene derived electrons fueled chlorobenzene dechlorination removing the need to provid
46 ng visible light CRA-S(N)Ar with unactivated chlorobenzene derivatives as the limiting reagent.
47  of certain HiPco SWNTs upon reaction with 4-chlorobenzene diazonium and 4-hydroxybenzene diazonium s
48 toluminescence (PL) during a reaction with 4-chlorobenzene diazonium in aqueous solution, evidence fo
49  including aromatic hydrocarbons (mixture of chlorobenzene-h(5) and chlorobenzene-d(5), mixture of 1,
50 here 5x10(8)cells/ml degraded 125 nmol/ml of chlorobenzene in 150 min.
51 nmental fate of nitro- and amino-substituted chlorobenzenes in complex aqueous samples.
52 inated the overall partitioning of the three chlorobenzenes in the 1.5 mum filtrate, and the partitio
53  in the context of mineral phases along with chlorobenzenes in the green corrosion.
54 rmediate biodegradation products benzene and chlorobenzene increased and achieved steady state values
55                                              Chlorobenzene is a widespread groundwater contaminant fo
56 E of devices processed by high-boiling point chlorobenzene is less than 2%.
57 on acceptors tested, and dehalogenated every chlorobenzene isomer except 1,4-DCB.
58 and honokiol trapped two peroxyl radicals in chlorobenzene (kinh = 3.8 x 10(4) M(-1) s(-1)) and four
59 d catalytic amounts of pyridine in refluxing chlorobenzene leads to the formation of acyl chlorides.
60 he nanostructures in the droplet-based water-chlorobenzene MEs were in the range of 1 to 11 nm.
61 iate chlorine atoms from individual oriented chlorobenzene molecules adsorbed on a Si(111)-7 x 7 surf
62 he use of silver, previously unexplored, and chlorobenzene-normally regarded as relatively inert in s
63       Crystals of BA were grown in o-xylene, chlorobenzene, o-dichlorobenzene, and benzonitrile, as w
64 orption and reactions of phenylacetylene and chlorobenzene on Ag(100).
65 fBT4T-2OD, and PffBTff4T-2DT) in solution in chlorobenzene or dichlorobenzene.
66 y 1,1'-(2,2,2-trichloroethane-1,1-diyl)bis(4-chlorobenzene), or 4,4'-DDT] manufacture occurred histor
67 is shows that p-SIDT(FBTTh2)2 spin-cast from chlorobenzene organizes into crystalline domains with la
68 her industrial or byproduct organochlorines (chlorobenzenes, pentachloroanisole, octachlorostyrene),
69 xadiene (CHD) as convenient HOO(*) source in chlorobenzene (PhCl) or acetonitrile solutions containin
70                                 In refluxing chlorobenzene pure 1b was converted to the more thermody
71                  Reductive dechlorination of chlorobenzene requires input of electron donor and resul
72  of other dopants, such as fluorobenzene and chlorobenzene, shifted the ionization toward radical cat
73 tical lamotrigine and the industrial solvent chlorobenzene, signifying that electrocatalytic treatmen
74 romonomers 16 in the presence of end-capping chlorobenzene solvent to produce the statistical spacerl
75 Enumeration of bacteria capable of degrading chlorobenzenes suggested that most of the biodegradation
76                     Analog 14, featuring a 2-chlorobenzene sulfonamide cap, demonstrated a 120-fold e
77 lion (3-[2,4 dihydroxyphenylazo]-2-hydroxy-5-chlorobenzene sulfonic acid), the DNA stain 4',6-diamino
78 in the order of toluene ( t(1/2) = 4.6 min), chlorobenzene ( t(1/2) = 14.0 min), dichloromethane ( t(
79 rs rely heavily on solvent, with polymers in chlorobenzene taking six times as long to degrade as in
80 ylbenzene, carbon tetrachloride, chloroform, chlorobenzene, tetrachlorethane, and dichlorobenzene.
81 aminants, e.g., nitro- and amino-substituted chlorobenzenes that are widely used as industrial feedst
82 lture capable of reductive dechlorination of chlorobenzene to benzene with a second benzene-degrading
83 ing from simple aromatics (e.g., aniline and chlorobenzene) to the much larger squalene (M(w) = 411)
84 efficiently than alpha-tocopherol in a water/chlorobenzene two-phase system containing N-acetylcystei
85 ombination resulted in the transformation of chlorobenzene via benzene to the nontoxic degradation pr
86       The dispersions were composed of water-chlorobenzene (water analysis) and water-oleic acid (mon
87  more efficiently than alpha-tocopherol in a chlorobenzene/water two-phase system.
88                                  Benzene and chlorobenzene were treated aerobically on site in an exi
89 redominantly forms protonated molecules, and chlorobenzene, which favors the formation of radical cat
90 ch 1,2-dithienyl-1,2-dicyanoethene (4TCE) in chlorobenzene with ultrafast transient absorption spectr
91 alogenation capability of each strain to use chlorobenzenes with three or more chlorines, tetrachloro
92                   Spincasting GRIM POPT from chlorobenzene yields a thin film with a 1.8 eV band gap,