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1 ndary benzylic C-H bonds, such as toluene or ethylbenzene.
2 , and even into a benzylic sp(3) C-H bond of ethylbenzene.
3 ansfer the H(+)/H(-) pair to styrene to give ethylbenzene.
4 ogenation sequence directly from alkanes and ethylbenzene.
5 phenylacetylene, naphthalene, and 1-chloro-4-ethylbenzene.
6  product, primarily o-xylene and secondarily ethylbenzene.
7 ohexene, and k = 7.7 x 10(4) M(-1) s(-1) for ethylbenzene.
8 n EB1 cells that were grown anaerobically on ethylbenzene, 1-phenylethanol, and acetophenone, but the
9  10-ethanoanthracene-11, 12-dicarboximido)-4-ethylbenzene-1, 2-diol (DEDE) and NiO/CNTs nanocomposite
10 arylacetylenes (phenylacetylene; 1-ethynyl-2-ethylbenzene; 1-ethynyl-2,4,6-R(3)-benzene (R = Me, Et,
11  isotope fractionation for benzene, toluene, ethylbenzene, 2,6-dichlorobenzamide, and metolachlor at
12 ired from samples of 1-butanol (55 nmol) and ethylbenzene (250 nmol).
13 EX compounds (benzene, toluene, xylenes, and ethylbenzene), 40%; other VOC aromatics, 15%.
14 vities vary with arene as mesitylene, 99%, > ethylbenzene, 86% > toluene, 67%.
15 ize a previously inaccessible BN isostere of ethylbenzene, a compound of interest in biomedical resea
16 rogen to assess different means of microbial ethylbenzene activation.
17 heir co-occurrence with hydrocarbons such as ethylbenzene and butane.
18  [Cl2NN]Cu-NHAr with hydrocarbons R-H (R-H = ethylbenzene and cyclohexane) reveals inefficient stoich
19 zene as an internal standard in a mixture of ethylbenzene and cyclohexanone in hexane with analyte qu
20                                              Ethylbenzene and cyclohexanone of a single D enrichment
21 d the kinetic isotope effect in oxidation of ethylbenzene and ethylbenzene-d(10) is k(H)/k(D) = 2.3.
22 ere ranked based on their correlation toward ethylbenzene and gefitinib.
23 the hydrophenylation of ethylene to generate ethylbenzene and isomers of diethylbenzene.
24 nging isomers of similar volatility, such as ethylbenzene and m/ p-xylene.
25  It is shown that the two structural isomers ethylbenzene and p-xylene can be discriminated by REMPI
26 w/w) the PMMA film was more sensitive toward ethylbenzene and p-xylene over naphthalene when compared
27 diate behavior (with 40-60% efficiency), and ethylbenzene and styrene were completely transferred (10
28 catalyst is versatile for dehydrogenation of ethylbenzene and tetrahydroquinoline as well as for hydr
29  dehydrogenase was found to oxidize 4-fluoro-ethylbenzene and the nonaromatic hydrocarbons 3-methyl-2
30 atography (HPLC-UV), BTEX (Benzene, Toluene, Ethylbenzene and Xylenes) by gas chromatoghaphy (GC-FID)
31 een HO(*) or SO(4)(*-) and benzene, toluene, ethylbenzene, and (BTEX) xylene isomers.
32 al-initiated oxidation of toluene, p-xylene, ethylbenzene, and benzene was investigated in a series o
33        Nonpolar compounds, benzene, toluene, ethylbenzene, and o-xylene (BTEX) and polar compounds, p
34            Model compounds benzene, toluene, ethylbenzene, and o-xylene (BTEX) are conveniently and r
35 l tert-butyl ether (MTBE), benzene, toluene, ethylbenzene, and o-xylene (BTEX), and analysis of delta
36 ert-butyl ether (MTBE) and benzene, toluene, ethylbenzene, and p-xylenes (BTEX).
37 , aniline, phenol, phenylacetylene, styrene, ethylbenzene, and phenylhydrazine.
38 n = 49) sets, three compounds (acetophenone, ethylbenzene, and styrene) distinguished between patient
39 ncluding the BTEX mixture (benzene, toluene, ethylbenzene, and the regioisomers of xylene), into thei
40 ion plant for detection of benzene, toluene, ethylbenzene, and the three structural isomers of xylene
41              Mean regional benzene, toluene, ethylbenzene, and total xylenes (BTEX) concentrations in
42 larger than C(1)-C(5) were benzene, toluene, ethylbenzene, and total xylenes at concentrations up to
43 ere determined for hexane, benzene, toluene, ethylbenzene, and xylene (BTEX compounds).
44                            Benzene, toluene, ethylbenzene, and xylene (BTEX) are retrieved during fos
45 ontent (largely made up of benzene, toluene, ethylbenzene, and xylene (BTEX)) was a more accurate pre
46  trichloroethene (TCE) and benzene, toluene, ethylbenzene, and xylene (BTEX).
47 ); black carbon (BC); NO2; benzene, toluene, ethylbenzene, and xylene (BTEX); carbonyl compounds; and
48 ndustrially relevant BTEX (benzene, toluene, ethylbenzene, and xylene isomers) mixture.
49 aromatic species: benzene, toluene, styrene, ethylbenzene, and xylene.
50 sed by the introduction of benzene, toluene, ethylbenzene, and xylenes (BTEX) and ethanol mixtures un
51  Angeles, illustrating how benzene, toluene, ethylbenzene, and xylenes (BTEX) and isoprene, along wit
52 minated water, they sorbed benzene, toluene, ethylbenzene, and xylenes (BTEX) and then desorbed the c
53 e emissions, with combined benzene, toluene, ethylbenzene, and xylenes (BTEX) concentrations totaling
54                            Benzene, toluene, ethylbenzene, and xylenes (BTEX) included in a 39-compon
55  from 80 to <0.01 mg/L and benzene, toluene, ethylbenzene, and xylenes (BTEX) reductions to below det
56 en PFI and GDIs, including benzene, toluene, ethylbenzene, and xylenes (BTEX).
57  detection and analysis of benzene, toluene, ethylbenzene, and xylenes (BTEX).
58 dustries emitting styrene, benzene, toluene, ethylbenzene, and xylenes (SBTEX).
59        The strain degraded benzene, toluene, ethylbenzene, and xylenes at salinities ranging from 0.0
60 e direct flux estimates of benzene, toluene, ethylbenzene, and xylenes from upstream O&G production f
61 of low concentrations (1-60 ppm) of toluene, ethylbenzene, and xylenes in water.
62                            Benzene, toluene, ethylbenzene, and xylenes were detected in 99.7% of surf
63 that personal exposures to benzene, toluene, ethylbenzene, and xylenes were dominated by a specific w
64 ormaldehyde, acetaldehyde, benzene, toluene, ethylbenzene, and xylenes were measured.
65 ane (C(6)-C(10)) and BTEX (benzene, toluene, ethylbenzene, and xylenes) components using primary enri
66 cular, the BTEX compounds (benzene, toluene, ethylbenzene, and xylenes), in the low milligrams/liters
67 erest, the BTEX compounds (benzene, toluene, ethylbenzene, and xylenes), which are common indicators
68 c compounds (VOCs) such as benzene, toluene, ethylbenzene, and xylenes, and chlorinated solvents (e.g
69 c compounds (VOCs, such as benzene, toluene, ethylbenzene, and xylenes, or BTEX), and account for the
70  the cyclam chelate and the substrate (e.g., ethylbenzene) associated with the equatorial pi-attack r
71 onger for, respectively, p-xylene, o-xylene, ethylbenzene, benzene, m-xylene and toluene.
72 ortho-, meta-, and para-xylene isomers), and ethylbenzene (BTEX) are associated with an increased inc
73 nocytes for 5 days with benzene, xylene, and ethylbenzene, but not toluene, fostered a consistent pro
74 re dominated by an Azoarcus species activate ethylbenzene by anaerobic hydroxylation catalyzed by eth
75                  Anaerobic mineralization of ethylbenzene by the denitrifying bacterium Azoarcus sp.
76 es involving the stoichiometric amination of ethylbenzene by {[Cl2NN]Cu}2(mu-N(t)Bu) (3) demonstrate
77 s composed of toluene (C(7)H(8)), p-xylene + ethylbenzene (C(8)H(10)), 1,3,5-trimethylbenzene (C(9)H(
78 ances such as benzene, toluene, styrene, and ethylbenzene can be found as well.
79 te, used for the synthesis of chemicals like ethylbenzene, cumene, cyclohexane, nitrobenzene and alky
80 pears to apply to the oxidations of toluene, ethylbenzene, cumene, indene, and cyclohexene.
81 tope effect in oxidation of ethylbenzene and ethylbenzene-d(10) is k(H)/k(D) = 2.3.
82 arge KIE values were found for oxidations of ethylbenzene-d0 and -d10 at room temperature.
83 ctionation is a valuable tool to distinguish ethylbenzene degradation and may be of practical use for
84                                The anaerobic ethylbenzene degradation pathway of Aromatoleum aromatic
85                      The membrane-associated ethylbenzene dehydrogenase activity was found to oxidize
86                                         Both ethylbenzene dehydrogenase and 1-phenylethanol dehydroge
87      We developed in vitro assays to examine ethylbenzene dehydrogenase and 1-phenylethanol dehydroge
88                                     Purified ethylbenzene dehydrogenase contains approximately 0.5 mo
89 e analysis and biochemical data suggest that ethylbenzene dehydrogenase is a novel member of the dime
90                                  We purified ethylbenzene dehydrogenase to apparent homogeneity and s
91        In addition to ethylbenzene, purified ethylbenzene dehydrogenase was found to oxidize 4-fluoro
92 e reductase, dimethyl sulfide dehydrogenase, ethylbenzene dehydrogenase, and chlorate reductase, all
93 zene by anaerobic hydroxylation catalyzed by ethylbenzene dehydrogenase, similar to Aromatoleum aroma
94                                              Ethylbenzene dehydrogenase, which catalyzes this reactio
95 f Aromatoleum aromaticum is initiated by the ethylbenzene dehydrogenase-catalyzed monohydroxylation o
96 bdoenzyme family, the closest relative being ethylbenzene dehydrogenase.
97 exhibits high reactivity in the oxidation of ethylbenzene derivatives.
98 econd aromatic C-H activation competing with ethylbenzene dissociation.
99  benzene, toluene, m,p-xylene, o-xylene, and ethylbenzene) during VOC events.
100           The separation of styrene (ST) and ethylbenzene (EB) mixtures is of great importance in the
101 8 isomers, o-xylene (OX), m-xylene (MX), and ethylbenzene (EB).
102 parate a wide variety of mixtures, including ethylbenzene from styrene, haloaromatics, terpinenes, pi
103 ncluding xylenes, pinenes, benzene, toluene, ethylbenzene, hexane, pentane, chloroform, and carbon te
104  hydrogen isotope ratios caused by anaerobic ethylbenzene hydroxylation both mathematically and exper
105 compounds (i.e., TEX - toluene, xylenes, and ethylbenzene) in European urban areas.
106 selected petroleum hydrocarbons (toluene and ethylbenzene, in 1:2 mixtures of labeled (perdeuterated)
107  benzene (IRR = 3.86), toluene (IRR = 1.50), ethylbenzene (IRR = 5.16), p-xylene (IRR = 9.41), o-xyle
108 peroxo complex in the presence of toluene or ethylbenzene leads to rarely seen C-H activation chemist
109 ous crystals of the DB diacid monosalt of an ethylbenzene-linked piperazinium (DB-EtPh-Pz) lacking a
110 al rates exhibit saturation behavior at high ethylbenzene loadings and an inverse dependence on the c
111 sed to quantify mixtures containing toluene, ethylbenzene, m-xylene, naphthalene, and biphenyl from u
112 , SO(2), NO, NO(2), NO(X), benzene, toluene, ethylbenzene, m-xylene, p-xylene, o-xylene (BTEX), and B
113 , SO(2), NO, NO(2), NO(X), benzene, toluene, ethylbenzene, m-xylene, p-xylene, o-xylene, and BTEX dat
114            A tentative pathway for anaerobic ethylbenzene mineralization by strain EB1 is proposed.
115                  The first step in anaerobic ethylbenzene mineralization in denitrifying Azoarcus sp.
116 ng power of 1.57 at 10 ppb and 836 SV for an ethylbenzene monomer.
117 with significantly higher levels of benzene, ethylbenzene, o-xylene, and m-xylene.
118                An increase of 10 mug/m(3) in ethylbenzene, o-xylene, m-xylene, and 10 ppb of NO corre
119 [mg of protein](-1) and an apparent K(m) for ethylbenzene of approximately 60 microM.
120 kel-amide [Me(3)NN]Ni-N(CHMePh)Ad (3) (R-H = ethylbenzene) or aminoalkyl tautomer [Me(3)NN]Ni(eta(2)-
121 xtracts of Azoarcus sp. strain EB1 catalyzed ethylbenzene oxidation at a specific rate of 10 nmol min
122                                    Enzymatic ethylbenzene oxidation was stereospecific, with (S)-(-)-
123 ydroxyl group of the first product of anoxic ethylbenzene oxidation, 1-phenylethanol, is derived from
124  relevant model compounds (benzene, toluene, ethylbenzene, p-xylene, 1,2,4-trimethylbenzene, and naph
125 -ethylhexyl) phthalate for benzene, toluene, ethylbenzene, p-xylene, and naphthalene, respectively.
126 We advanced LUR models for benzene, toluene, ethylbenzene, p-xylene, m-xylene, o-xylene (BTEX), and t
127 ns, a systematic study of the nitrosation of ethylbenzene, phenethylamine, and tyramine was carried o
128 es of aromatic compounds, including toluene, ethylbenzene, phenol, benzoate, and dihydroxylated compo
129                               In addition to ethylbenzene, purified ethylbenzene dehydrogenase was fo
130 diazoacetates in the presence of substituted ethylbenzenes results in benzylic C-H activation by mean
131 benzene but was unable to transform 4-chloro-ethylbenzene, the ethyltoluenes, and styrene.
132 suspensions of strain EB1 cells metabolizing ethylbenzene, the transient formation and consumption of
133 led to the enantioselective hydroxylation of ethylbenzene to (R)-1-phenylethanol (99 % ee).
134  Azoarcus sp. strain EB1 is the oxidation of ethylbenzene to (S)-(-)-1-phenylethanol.
135  shown to be initiated by dehydrogenation of ethylbenzene to 1-phenylethanol.
136 as demonstrated by conversion of 69% of [14C]ethylbenzene to 14CO2.
137 on triggered the photocatalytic oxidation of ethylbenzene to acetophenone, which in turn was enantios
138              Cells of strain EB1 mineralized ethylbenzene to CO2 under denitrifying conditions, as de
139  material, redox-ODH auto-thermally converts ethylbenzene to styrene with up to 97% single-pass conve
140 ctions with benzylic substrates R-H (indane, ethylbenzene, toluene).
141 e/TSIL@MWCNTs), was used to extract benzene, ethylbenzene, toluene, and xylene (BTEX) from cow's milk
142 s included hydroxylations of benzyl alcohol, ethylbenzene, Tris buffer, lauric acid, and methyl laura
143 genation of phenylacetylene into styrene and ethylbenzene under modest conditions (1-50 bar H(2), 40-
144                          Hexane, octane, and ethylbenzene were also successfully converted to the cor
145  mixtures of benzene with toluene as well as ethylbenzene were characterized at concentrations below
146  Initial reactions in anaerobic oxidation of ethylbenzene were investigated in a denitrifying bacteri
147 , 13,200, 19,300, 31,600, and 90,000) and of ethylbenzene were measured by the method of moments.
148            Toluene, o-xylene, m/p-xylene and ethylbenzene were significantly associated with nasal ob
149 (kH/kD) for oxidations of benzyl alcohol and ethylbenzene were small, reflecting the increased reacti
150 ene and ethylene through the intermediacy of ethylbenzene, which must be dehydrogenated in a separate
151 ently undergo only one H/D exchange, whereas ethylbenzene, which protonates at a ring position of the
152 phenylacetylene, naphthalene, and 1-chloro-4-ethylbenzene) with SmI(2) in the presence of MeOH or TFE
153 he presence of contaminants such as toluene, ethylbenzene, xylene, 2,2,4-trimethyl-1,3-pentanediol di
154     Widespread exposure to benzene, toluene, ethylbenzene, xylene, and styrene (BTEXS) and the potent
155 l petroleum hydrocarbons and benzene-toluene-ethylbenzene-xylene measurements-both collected during s
156 ) often involve monitoring benzene, toluene, ethylbenzene, xylenes (BTEX), and styrene (BTEXS) becaus
157     The presence of BTEXS (benzene, toluene, ethylbenzene, xylenes and styrene) in virgin olive oils
158 f BTEX hydrocarbons (i.e., benzene, toluene, ethylbenzene, xylenes).
159  limits of detection were <1 pg for toluene, ethylbenzene, xylenes, and isopropylbenzene; the limit o
160 O, NOx, black carbon (BC), benzene, toluene, ethylbenzene-xylenes (BTEX), and size-resolved particle

 
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