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presents some literature data of catalytic oxidation of VOCs on the supported noble and base metal catalysts. It is seen that the noble metal catalysts are very active in toluene complete oxidation [ 2 , 4 , 28 ]. The best total toluene conversion
and dip coating from stable precursor sols. The sources for Ti 4+ and W 6+ ions are the respective metal chlorides, dissolved in ethanol. The choice of WCl 6 is based on literature data reporting that the photocatalytic activity of Ti(W)O x powder
conditions. In the present work, the reduction peak appeared at two major temperature ranges: 200–400 °C and 400–800 °C. According to the literature, the reduction of large Co 3 O 4 particles to Co metal and possibly partial reduction of highly dispersed Co
binding energies of Ru species (3d 5/2 ) found in the literature and this study BE of Ru 3d 5/2 (eV
aldehyde 5e reporting here is the highest compared to all previous reports in the literature. Table 4 Hydroformylation of different allylbenzene derivatives
components of the oil and separated fractions were identified by comparison of their linear retention indices, determined in relation to a homologous series of n -alkanes, with those from pure standards or reported in the literature. Comparison of
developed for fats and oils double bond hydrogenation and the existence of reasonable proposals for reaction pathways for selective hydrogenation of carboxymethyl groups, no such studies are found in the literature. Scheme 1
decreases with the increasing Si/Ti ratio, indicating that the Lewis acidic sites in samples are mainly from the highly-dispersed amorphous TiO x species. The results are consistent with the finding reported in the literature [ 24
and phenyl group. In all products, J 4a–10b was found to be 1.55–3.3 Hz indicating the cis junction between pyrane ring and quinoline moiety which is in accordance with literature values. The workup and catalyst recovery is very simple
compounds [ 4 ]. Analytical technology allows for an increasing number of PPCPs to be detected in STP effluents, surface water, ground water, drinking water, sludge, soil and aquatic organisms [ 5 – 8 ]. According to literature reports, the
