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OH oxidation

Sn Citrate, C20 , 2,3-dimercaptopropanol, EDTA, F , E, OH , oxidation with bromine water,... [Pg.1176]

MDR-ABC Transporters. Figure 3 Detoxification cellular mechanisms. X, toxic compound X-OH, oxidized toxic compound GS-X, conjugated toxic compound OATP, organic anion transporting proteins CYPs, cytochromes GSH, glutathion UDPGIcUA, Uridine 5-diphosphoglucuronic acid PAPs, 3-phosphoadenylylsulfate. [Pg.751]

OH/oxide species. At potentials anodic of 1 V, incomplete oxidation of formaldehyde to formic acid is activated, while methanol oxidation is almost completely hindered. This reflects an easier oxidation of the C-H group in the aldehyde than in the alcohol. For the negative-going scan, where the COadouble-peak stmcture in the current efficiency. [Pg.453]

Citrate, C20)-, 2,3-dimercaptopropanol, EDTA, F-, I-, OH-, oxidation with bromine water, phosphate(3—), tartrate, triethanolamine, thioglycolic acid Citrate, jV.jV-dihydroxyethylglycine, EDTA, F-, SO)-, tartrate Citrate, F-, H202, OH-, oxalate, tartrate Citrate, F-, I-, reducing agents, S2-, sulfite, tartrate... [Pg.1445]

The In situ spectrum obtained at 0.5 V vs. Hg/HgO,OH" (oxidized state) is shown in curve a, Fig. 7. Following this measurement, the potential was swept to 0.0 V (reduced state), and a new In situ spectrum recorded after the current had dropped to a very small value (curve b, Fig. 7). Essentially identical results were obtained when the films were examined first in the reduced and then in the oxidized state. [Pg.270]

MOOM, and MO-) that parallel those that result from "OH oxidation at the metal surfaces. ... [Pg.466]

Although water oxide, once formed, proved to be a remarkably efficient oxygen atom donor, it is quite likely that it is simply too high in energy to be a viable oxidant. A second problem with the preliminary calculations by Bach and coworkers" is that NH3 is not a realistic nucleophile for such studies it is what was feasible at that time. This inadequacy has only recently been ameliorated by Ottolina and Carrea , who used the more nucleophilic trimethylamine (TMA) as the attacking nucleophile and got an entirely different and much more chemically realistic hypersurface for the HO—OH oxidation of amines. The prior results at the MP2 level compared favorably with the results of the B3LYP/6-31-I-G method, so the basic problem was in the nucleophile and not with the... [Pg.68]

FIGURE 31. Transition structure for the HO—OH oxidation of dimethyl sulfide with three water molecules fully optimized at the B3LYP/6-31++G(d,p) level. The reaction barrier (A ) was calculated at the MP4//B3LYP/6-31-I— -G(d,p) level with respect to the reactant cluster... [Pg.71]

INTO HALF OF THE MANGANESE SUL-fXte SOLUTION YOU HAVE MADE, POUR 10% SOLUTION OF NaOH UNTIL NO MORE PRECIPITATE FORMS. WHITISH Mn[OH), OXIDIZES INTO BROWN MnO(OH). [Pg.66]

Measurements of these relatively minor species will not only complete the budget of NO, but will also indicate if our understanding of the hydrocarbon oxidation schemes in the atmosphere is complete. The organic nitrates that completed the NO, budget in the example in Figure 9 arose primarily from the oxidation of the naturally emitted hydrocarbon, isoprene (2-methylbutadiene). To demonstrate the oxidation mechanisms believed to be involved in the production of multifunctional organic nitrates, a partial OH oxidation sequence for isoprene is discussed. The reaction pathways described are modeled closely to those described in reference 52 for propene. The first step in this oxidation is addition of the hydroxyl radical across a double bond. Subsequent addition of 02 results in the formation of a peroxy radical. With the two double bonds present in isoprene, there are four possible isomers, as shown in reactions 2-5 ... [Pg.271]

Reference 52 organic nitrate produced via addition of an N03 radical. Reference 52 organic nitrate produced via OH oxidation of propene. [Pg.274]

The properties of O-, in contrast to these of the conjugated acid HO, are still poorly studied. The review by J. Lee and Grabowsky (1992) describes mass spectrometry of this radical. In conditions that are usual for synthetic organic chemistry, O- displays less reactivity than its acid OH. Oxidation of acetone by radicals O and OH leads to quite different products (Morkovnik Orhlobystin 1979) see combined Scheme 1-83 ... [Pg.63]


See other pages where OH oxidation is mentioned: [Pg.405]    [Pg.506]    [Pg.343]    [Pg.76]    [Pg.78]    [Pg.392]    [Pg.138]    [Pg.334]    [Pg.447]    [Pg.68]    [Pg.68]    [Pg.59]    [Pg.66]    [Pg.589]    [Pg.67]    [Pg.69]    [Pg.70]    [Pg.70]    [Pg.74]    [Pg.75]    [Pg.963]    [Pg.212]    [Pg.792]    [Pg.1252]    [Pg.67]    [Pg.68]    [Pg.69]    [Pg.70]    [Pg.70]    [Pg.74]    [Pg.75]    [Pg.963]    [Pg.50]    [Pg.168]    [Pg.368]    [Pg.519]    [Pg.85]    [Pg.313]   
See also in sourсe #XX -- [ Pg.429 , Pg.430 , Pg.431 , Pg.432 , Pg.493 ]




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OH-initiated oxidation

Oxidation Reaction Mechanism of Alkanes by OH

Oxidation Reaction Mechanism of Alkenes by OH

Oxidation Reaction Mechanism of Alkynes by OH

Oxidation by OH radical

Oxidation of Methane in the Natural Atmosphere and OH Radical Chain Reaction

Oxidations of Individual OH Groups

S(IV) Oxidation by the OH Radical

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