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SO2-SO3 oxidation

Sulfur in catalysis is an object of outstanding interest both as atom(s) in compounds being transformed catal3d,icaUy, and as a part of catalysts applied in chemical transformations, especially in hydrotreatment processes. Catalytic methods — both homogenous and heterogeneous — of sulfuric acid production were known before the concept of catalysis was formulated the heterogeneous SO2-SO3 oxidation was one of the phenomena leading Berzelius to introduce the concept and the name of catalysis. [Pg.63]

Some early observations on the catalytic oxidation of SO2 to SO3 on platinized asbestos catalysts led to the following observations (1) the rate was proportional to the SO2 pressure and was inversely proportional to the SO3 pressure (2) the apparent activation energy was 30 kcal/mol (3) the heats of adsorption for SO2, SO3, and O2 were 20, 25, and 30 kcal/mol, respectively. By using appropriate Langmuir equations, show that a possible explanation of the rate data is that there are two kinds of surfaces present, 5 and S2, and that the rate-determining step is... [Pg.741]

Another important example of a redox titration for inorganic analytes, which is important in industrial labs, is the determination of water in nonaqueous solvents. The titrant for this analysis is known as the Karl Fischer reagent and consists of a mixture of iodine, sulfur dioxide, pyridine, and methanol. The concentration of pyridine is sufficiently large so that b and SO2 are complexed with the pyridine (py) as py b and py SO2. When added to a sample containing water, b is reduced to U, and SO2 is oxidized to SO3. [Pg.345]

Salts are obtained by direct neutralization of the acid with appropriate oxides, hydroxides, or carbonates. Sulfamic acid is a diy, non-volatile, non-hygroscopic, colourless, white, crystalline solid of considerable stability. It melts at 205°, begins to decompose at 210°, and at 260° rapidly gives a mixture of SO2, SO3, N2, H2O, etc. It is a strong acid (dissociation constant 1.01 x 10 at 25° solubility 25gper 100g H2O) and, because of its physical form and stability, is a convenient standard for acidimetry. Over 50000 tonnes are manufactured annually and its principal applications are in formulations for metal cleaners, scale removers, detergents and stabilizers for chlorine in aqueous solution. [Pg.742]

Volcanic gases contain up to 47% sulphur dioxide (SO2). A group from the University of Hong Kong studied the ability of SO2 to support condensation reactions. Under weakly basic conditions, SO2 dissolved in water forms SO2- ions. Oxidation of these to SO4- proceeds via SO3. The experiments suggest the following reaction mechanism ... [Pg.134]

These polar transformation products and sulfur oxides (SO2, SO3) arising in the ultimate stages of the transformation process are formed in trace amounts in the aged polymer matrix. Volatile products may be sources of undesirable organoleptic problems. This limits the use of organic thiocompounds in odor-sensitive applications. Organic S-proto-nic acids 85, 86 deactivate basic stabilizers (HAS). The peroxidolytic effect of 85, 86 is reduced in the presence of some antiacids or fillers, e.g., calcium carbonate. [Pg.74]

Most likely the changes in IEP value, as well as in PCD potential, during the enzymatic treatment of wool are the result of enzyme-initiated oxidation reactions. As can be seen from the XPS results specified below (Table 1), a slight increase in SO2, SO3, SO4 groups concentration, from 0.248% (0.248%= 11.8% of 2.1% of total elemental concentration) for untreated sample to 0.314% (0.314% = 19.6% of 1.6% of total elemental concentration) can be observed. [Pg.135]

Flow of -700 K SO2/SO3 bearing gas around the loaded catalyst causes it to form a vanadium oxide-alkali metal pyrosulfate melt on the surfaces of the catalyst s porous silica substrate. [Pg.92]

Table 21.1. Bottom half of Table O.l s 3rd catalyst bed heatup path-equilibrium curve intercept worksheet. Input and output gas enthalpies are shown in rows 43 and 44. Note that they are the same. This is because our heatup path calculations assume no convective, conductive or radiative heat loss during catalytic SO2+V2O2 —> SO3 oxidation, Section 11.9. 1st and 2nd catalyst bed enthalpies are calculated similarly - using Tables J.2 and M.2. [Pg.238]

The sulfur oxides include the simplest species SO, SO2, SO3 through to very sulfur-rich species such as SgO (Figure 12), although the di- and trioxide are undoubtedly the... [Pg.4616]

OSHA PEL CL 5 mg(Mn)/m3 ACGIH TLV TWA 0.03 mg(Mn)/m3 SAFETY PROFILE Poison by intraperitoneal route. Quesdonable carcinogen with experimental neoplasdgenic data. An experimental teratogen. Experimental reproduedve effects. Mutadon data reported. When heated to decomposidon it emits toxic fumes of SO2, SO3, and Mn oxides. See also MANGANESE COMPOUNDS and SULFATES,... [Pg.861]

The SCR process consists of the reduction of NO (typically 95% NO and 5% NO2 v/v) with NH3. The reaction stoichiometry is usually represented as 4NO + 4NH3 + 02 4N2 + 6H2O. This reaction is selectively effected by the catalyst, since the direct oxidation of ammonia by oxygen is prevented In the case of the treatment of sulfur-containing gas streams, the DcNO reaction is accompanied by the catalytic oxidation of SO2 to SO3 Oxidation of SO2 is highly undesirable because SO3 is known to react with water and residual ammonia to form ammonium sulfates, which can damage the process equipment. [Pg.122]

DeNOx reaction involves a strongly adsorbed NH3 species and a gaseous or weakly adsorbed NO species, but differ in their identification of the nature of the adsorbed reactive ammonia (protonated ammonia vs. molecularly coordinated ammonia), of the active sites (Br0nsted vs. Lewis sites) and of the associated reaction intermediates [16,17]. Concerning the mechanism of SO2 oxidation over DeNOxing catalysts, few systematic studies have been reported up to now. Svachula et al. [18] have proposed a redox reaction mechanism based on the assumption of surface vanadyl sulfates as the active sites, in line with the consolidated picture of active sites in commercial sulfuric acid catalysts [19]. Such a mechanism can explain the observed effects of operating conditions, feed composition, and catalyst design parameters on the SO2 SO3 reaction over metal-oxide-based SCR catalysts. [Pg.123]

Heteroatonuc contaminants present in the gas and the tar, like Cl and S, react with the metals at the surface of the catalyst. The process is known as catalyst poisoning because the salts formed are not showing catalytic activity towards tar reforming. Some of this poisoning, basically the one associated with the S can be reversible because hi regeneration temperatures can transform the sulfides to sulfates and subsequently decompose the sulfates to SO2/SO3 and the corresponding metal oxides. This is not the case with Cl. [Pg.1678]

Vanadium plays an important role in many industrial catalysts used extensively in a variety of applications including the production of SO3 from SO2, selective oxidation of hydrocarbons, reduction of nitrogen oxides with ammonia, and in the manufacture of many chemicals and chemical intermediates. Such catalysts typically consist of vanadium compounds supported on oxides such as silica, alumina, titania, etc., and their activity depends on factors such as the chemical form and crystalline environment... [Pg.646]

In Denmark the new SNOX process has been developed by Agerholm et al. [153]. Flue gases with a temperature of about 653 K are cleaned from NO by means of selective catalytic reduction. The gas is reheated up to 673 K and introduced to an SO2 converter which is located downstream from the SCR reactor. SO2 is oxidized into SO3 which is converted to sulfuric acid. The ammonia slip from the SCR reactor is oxidized simultaneously. Advantages of the SNOX process are ... [Pg.167]

On the basis of oxidation number considerations, one of the following oxides would not react with molecular oxygen NO, N2O, SO2, SO3, P40g. Which one is it Why ... [Pg.146]

Polonium is a radioactive element that is difficult to study in the laboratory.) Oxygen has a tendency to accept two electrons to form the oxide ion (O ) in many ionic compounds. Sulfur, selenium, and tellurium also form dinegative anions (S, Se, and Te ). The elements in this group (especially oxygen) form a large number of molecular compounds with nonmetals. The important compounds of sulfur are SO2, SO3, and H2S. Sulfuric acid is formed when sulfur trioxide reacts with water ... [Pg.315]

The tremendous force of a volcanic emption carries a sizable amount of gas into the stratosphere. There SO2 is oxidized to SO3, which is eventnally converted to sulfuric acid aerosols in a series of complex mechanisms. In addition to destroying ozone in the stratosphere (see p. 700), these aerosols can also affect climate. Because the stratosphere is above the atmospheric weather patterns, the aerosol clouds often persist for more than a year. They absorb solar radiation and thereby cause a drop in temperature at Earth s surface. However, this cooling effect is local rather than global, because it depends on the site and frequency of volcanic emptions. [Pg.705]

Metal oxide catalysts are extensively employed in the chemical, petroleum and pollution control industries as oxidation catalysts (e.g., oxidation of methanol to formaldehyde, oxidation of o-xylene to phthalic anhydride, ammoxidation of propylene/propane to acrylonitrile, selective oxidation of HjS to elemental sulfur (SuperClaus) or SO2/SO3, selective catalytic reduction (SCR) of NO, with NHj, catalytic combustion of VOCs, etc.)- A special class of metal oxide catalysts consists of supported metal oxide catalysts, where an active phase (e.g., vanadium oxide) is deposited on a high surface area oxide support (e.g., alumina, titania, ziiconia, niobia, ceria, etc.). Supported metal oxide catalysts provide several advantages over bulk mixed metal oxide catalysts for fundamental studies since (1) the number of surface active sites can be controlled because the active metal oxide is 100% dispersed on the oxide support below monolayer coverage,... [Pg.305]


See other pages where SO2-SO3 oxidation is mentioned: [Pg.366]    [Pg.53]    [Pg.81]    [Pg.81]    [Pg.366]    [Pg.53]    [Pg.81]    [Pg.81]    [Pg.13]    [Pg.22]    [Pg.611]    [Pg.420]    [Pg.3891]    [Pg.97]    [Pg.409]    [Pg.421]    [Pg.226]    [Pg.348]    [Pg.132]    [Pg.212]    [Pg.141]    [Pg.207]    [Pg.184]    [Pg.484]    [Pg.485]    [Pg.485]    [Pg.805]    [Pg.345]    [Pg.550]    [Pg.893]    [Pg.3890]   
See also in sourсe #XX -- [ Pg.6 , Pg.71 ]




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Assumptions in SO2 oxidation calculations 100% SO3 utilization during

Oxidation of SO2 to SO3 - Equilibrium curves

SO2

SO3 concentrations in industrial gases SO2 oxidation efficiency affected

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