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Aromatic oxidation benzene

In addition to nonheme iron complexes also heme systems are able to catalyze the oxidation of benzene. For example, porphyrin-like phthalocyanine structures were employed to benzene oxidation (see also alkane hydroxylation) [129], Mechanistic investigations of this t3 pe of reactions were carried out amongst others by Nam and coworkers resulting in similar conclusions like in the nonheme case [130], More recently, Sorokin reported a remarkable biological aromatic oxidation, which occurred via formation of benzene oxide and involves an NIH shift. Here, phenol is obtained with a TON of 11 at r.t. with 0.24 mol% of the catalyst. [Pg.101]

Reactions of partial electrochemical oxidation are of considerable interest in the electrosynthesis of various organic compounds. Thus, at gold electrodes in acidic solutions, olefins can be oxidized to aldehydes, acids, oxides, and other compounds. A good deal of work was invested in the oxidation of aromatic compounds (benzene, anthracene, etc.) to the corresponding quinones. To this end, various mediating redox systems (e.g., the Ce /Ce system) are employed (see Section 13.6). [Pg.283]

Of the alkenes (Figure 5.5) only ethene has been detected and of the aromatics only benzene has been seen unambiguously surprisingly propene has not been seen despite its well-understood microwave spectrum. Of interest to the origins of life is the onset of polymerisation in HCN to produce cyanopolyynes. These molecules could provide a backbone for the formation of information-propagating molecules required for self-replication. The survival of these species in a planetary atmosphere depends on the planet oxidation would be rapid in the atmosphere of today s Earth but what of the early Earth or somewhere altogether more alkane-based such as Titan ... [Pg.118]

Chemical/Physical. Under atmospheric conditions, the gas-phase reaction of o-xylene with OH radicals and nitrogen oxides resulted in the formation of o-tolualdehyde, o-methylbenzyl nitrate, nitro-o-xylenes, 2,3-and 3,4-dimethylphenol (Atkinson, 1990). Kanno et al. (1982) studied the aqueous reaction of o-xylene and other aromatic hydrocarbons (benzene, toluene, w and p-xylene, and naphthalene) with hypochlorous acid in the presence of ammonium ion. They reported that the aromatic ring was not chlorinated as expected but was cleaved by chloramine forming cyanogen chloride. The amount of cyanogen chloride formed increased at lower pHs (Kanno et al., 1982). In the gas phase, o-xylene reacted with nitrate radicals in purified air forming the following products 5-nitro-2-methyltoluene and 6-nitro-2-methyltoluene, o-methylbenzaldehyde, and an aryl nitrate (Chiodini et ah, 1993). [Pg.1153]

The incorporation of vanadium(V) into the framework positions of silicalite-2 has been reported by Hari Prasad Rao and Ramaswamy . With this heterogeneons oxidation catalyst the aromatic hydroxylation of benzene to phenol and to a mixtnre of hydroqninone and catechol conld be promoted. A heterogeneons ZrS-1 catalyst, which has been prepared by incorporation of zirconinm into a silicalite framework and which catalyzes the aromatic oxidation of benzene to phenol with hydrogen peroxide, is known as well in the literature. However, activity and selectivity were lower than observed with the analogous TS-1 catalyst. [Pg.528]

The photocatalyzed oxidation of gas-phase contaminants in air has been demonstrated for a wide variety of organic compounds, including common aromatics like benzene, toluene, and xylenes. For gas-phase aromatic concentrations in the sub-lOO-ppm range, typical of common air contaminants in enclosed spaces (office buildings, factories, aircraft, and automobiles), photocatalytic treatment leads typically to complete oxidation to CO2 and H2O. This generality of total destruction of aromatic contaminants at ambient temperatures is attractive as a potential air purification and remediation technology. [Pg.249]

Oxidation to Quinones. Direct oxidation of arenes to quinones can be accom-plished by a number of reagents. Very little is known, however, about the mechanism of these oxidations. Benzene exhibits very low reactivity, and its alkyl-substituted derivatives undergo benzylic oxidation. Electrochemical methods appear to be promising in the production of p-benzoquinone.797 In contrast, polynuclear aromatic compounds are readily converted to the corresponding quinones. [Pg.496]

Oxidation of Benzene Because of the complexity of the aromatics chemistry, large uncertainties remain in the oxidation mechanisms for even the simplest aromatic species, benzene and toluene [12,113]. The overall oxidation behavior (i.e., the fuel consumption rate) can be calculated with some confidence, but predictions of the concentration of intermediate species may be off by orders of magnitude. [Pg.602]

Even though details of the oxidation chemistry of even the simplest aromatic species, benzene and toluene, remain uncertain, reaction mechanisms are useful in evaluating the overall oxidation behavior of these fuels. Taking benzene as a characteristic compound, evaluate whether the conditions ensure complete oxidation of aromatic species. Use the supplied mechanism (benzen. mec [12]) or another recent mechanism for benzene oxidation, and assume plug flow. Assess whether the regulation could be less severe in terms of temperature or residence time if the reactants are completely mixed. [Pg.684]

In cyclic sulfoximides such as 3-ethoxy-4,5-dihydro-3-oxo-l-phenyl-and 3,4,5,6-tetrahydro-3,5-dioxo-1 -phenyl-1H-1 A6,2,4-thiadiazine 1 -oxides (46), the C6 proton signals appear at much higher fields [4.35 and 4.9 ppm (2H)] than for aromatic systems [benzene, 7.27 ppm thiophene, 7.2 (C2-H) and 6.95 ppm (C3-H)]. Similarly, the, 3C-NMR signals of the C6 atom appear at higher fields. These facts suggest a degree of ylidic character (77JOC952), which can be demonstrated by the reactivity of such compounds towards electrophiles (see Section III, C,3,f). [Pg.285]

Based on their chemical structure, the organic chemicals were divided into a number of categories alkanes, alkenes, amines, aromatic hydrocarbons, benzenes, carboxylic acids, halides, phenols, and sulfonic acid. Linear regression analysis has been applied using the method of least-squares fit. Each correlation required at least three datapoints, and the parameters chosen were important to ensure comparable experimental conditions. Most vital parameters in normalizing oxidation rate constants for QSAR analysis are the overall liquid volume used in the treatment system, the source of UV light, reactor type, specific data on substrate concentration, temperature, and pH of the solution during the experiment. [Pg.270]

Many organic compounds react with carboxylic acids, acyl halides, or anhydrides in the presence of certain metallic halides, metallic oxides, iodine, or inorganic acids to form carbonyl compounds. The reaction is generally applicable to aromatic hydrocarbons. Benzene, alkylbenzenes, biphenyl, fluorene, naphthalene, anthracene, acenaphthene, phenanthrene, higher aromatic ring systems, and many derivatives undergo the reaction. [Pg.610]

Potassium dichromate, K2Cr207, is applied under similar conditions as its sodium analogue to oxidize benzene rings to quinones [647, 648, 649, 650], methylene groups adjacent to aromatic rings to carbonyls [514], primary alcohols to aldehydes [651, 652, 653], secondary alcohols to ketones [644, 652, 654, 655], and aldehydes to acids [656]. Phenylhydroxylamine is transformed into nitrosobenzene [657], and an aromatic nitroso compound, into a nitro compound [655]. [Pg.24]

The degradation schemes of four aromatic hydrocarbons benzene, toluene, /7-xylene and 1,3,5-trimethylbenzene, have been updated on the basis of new kinetic and mechanistic data from current literature and conference proceedings and are available as part of the latest version of the Master Chemical Mechanism (MCMv3.1) via the MCM website thttn //mcm.leeds.ac.uk/MCM). The performance of these schemes concerning ozone formation from tropospheric aromatic oxidation has been evaluated using detailed environmental chamber datasets from the two EU EXACT measurement campaigns at EUPHORE (EXACT I - September 2001 and EXACT II - My 2002 (Pilling et al, 2003)). [Pg.143]

URANIUM HEXAFLUORIDE (7783-81-5) FjU Radioactive. Violent reaction with water, steam, ethanol, producing hydrogen fluoride gas. Violent reaction with alcohols, aromatic hydrocarbons (benzene, toluene, xylenes, etc.), bromine trifluoride. Aqueous solution increases the explosive sensitivity of nitromethane and is incompatible with sulfuric acid, alkalis, alcohols, ammonia, aliphatic amines, alkanolamines, alkylene oxides, amides, epichlorohydrin, ethers. [Pg.1066]

Although the aromatic compounds undergo hydrogen elimination readily upon oxidation [benzene (15) and naphthalene (16) can be polymerized electrochemically binaphthyl is formed in the thermal decomposition of bis(naphthalene)hexafluorophosphate], the analogous elimination of F+ in the fluoroaromatic compounds is not energetically feasible. [Pg.181]


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See also in sourсe #XX -- [ Pg.99 , Pg.100 , Pg.101 , Pg.102 , Pg.103 , Pg.104 , Pg.105 , Pg.106 ]




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