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1 n toluene or the first or second C-H BDEs in m-xylene.
2 anaerobic mineralization of both toluene and m-xylene.
3 iding in the active site simultaneously with m-xylene.
4 amoylmethyl)-1,4,7,10-tetraazacyclododecane]-m-xylene (1), 1,4-bis[1-(4,7,10-tris(carbamoylmethyl)-1,
5 , triethylamine, acetonitrile, formaldehyde, m-xylene, 2,2,2-trifluoroethylamine) were tested using t
6     The solvents used were benzene, toluene, m-xylene, 2,2,4-trimethylpentane (isooctane), decane, do
7 ll, as incubations containing both 15 microM m-xylene-alpha- (2)H 3 and 200 microM p-xylene resulted
8 bs values for CYP2E1 and CYP2A6 oxidation of m-xylene-alpha- (2)H 3 and p-xylene-alpha- (2)H 3 were d
9    CYP2A6 exhibited cooperative kinetics for m-xylene-alpha- (2)H 3 oxidation and a concentration-dep
10 th the degradation of biphenyl, naphthalene, m-xylene, and p-cresol are predicted to be distributed a
11  Reaction of HgCl(2) with MCl(3) in benzene, m-xylene, and p-xylene results in the formation of liqui
12 endent decrease in the reorientation rate of m-xylene, as no increase in ( k H/ k D) obs was observed
13 onent of TP2, i.e., 4,6-bis(4-hydroxyphenyl)-m-xylene (BX), deduced by simple structural reduction, i
14 at least 15% of the specific rate of in vivo m-xylene consumption.
15 obenzene-d(5), toluene-d(8), o-xylene-d(10), m-xylene-d(10), p-xylene-d(10), or mesitylene-d(12).
16                       Permeabilized cells of m-xylene-grown Azoarcus sp. strain T catalyzed the addit
17 abilized cells and whole-cell suspensions of m-xylene-grown Azoarcus sp. strain T demonstrated that t
18  of (i) a gaseous compound used as a tracer, m-xylene; (ii) one of the OH radical precursors, DMB.
19 that anaerobic oxidation of both toluene and m-xylene is initiated by addition of the aromatic hydroc
20 ter), o-xylene (kcat approximately 0.8 s-1), m-xylene (kcat approximately 0.6 s-1), and other aromati
21 ), benzene (B), toluene (T), p-xylene (p-X), m-xylene (m-X), o-xylene (o-X), styrene (S), o-cresol (o
22 en prepared by protonating benzene, toluene, m-xylene, mesitylene, and hexamethylbenzene with the car
23 of this enzyme in both anaerobic toluene and m-xylene mineralization.
24 y mixtures containing toluene, ethylbenzene, m-xylene, naphthalene, and biphenyl from unresolved chro
25 or benzene, toluene, ethylbenzene, p-xylene, m-xylene, o-xylene (BTEX), and total BTEX using measurem
26 s benzene, fluorobenzene, toluene, o-xylene, m-xylene, or p-xylene and the incoming arene is C(6)D(6)
27     The initial enzymatic steps in anaerobic m-xylene oxidation were studied in Azoarcus sp. strain T
28 g undergo cycloreversion at 150 degrees C in m-xylene solvent to form transient alpha-oxo-ortho-quino
29 Azoarcus sp. strain T anaerobically oxidizes m-xylene to 3-methylbenzoate (or its CoA thioester) via
30 arcus sp. strain T catalyzed the addition of m-xylene to fumarate to form (3-methylbenzyl)succinate.
31 nitrifying bacterium capable of mineralizing m-xylene via 3-methylbenzoate.
32 ehavior of the structure toward p-xylene and m-xylene was studied, and the results indicated that the
33 vative, 2-nitro-1,3-dimethylbenzene (2-nitro-m-xylene), was chosen as an internal standard for GC ana
34 denitrifying conditions on either toluene or m-xylene, while growth on benzoate was unaffected.

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