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Conversion to sulfate

Seheme 1 describes the evolution of samples LaCoOs (I) and LaCoOs (III) during the two poisoning regimes (LaCoOs (II) is intermediate between these two and therefore not represented). It shows that the differences in morphology of the fresh samples yield differences in the conversion to sulfate necessary to reach the end of the first regime as well as differences in this conversion at complete deactivation (end of the second regime). [Pg.48]

Darensbourg MY, Tuntulani T, Reibenspies JH (1995) Structure/function relationships in ligand-based S02/02 conversion to sulfate as promoted by nickel and palladium thiolates. Inorg Chem 34 6287-6294... [Pg.53]

An important step towards treatment of SO2 conversion to sulfate and deposition of both species that avoids absolute uncertainties of dispersion and deposition rates was taken by Lewis and Stevens, who investigated the mathematical basis of one form of hybrid receptor modeling (.16). Their model assumes that one measures concentrations of SO2 and SO4 relative to that of some species borne by particles from the plant. They assumed that (1) dispersion, deposition and transformation of the three species (SO2, SO4 and fine primary particles) are linear or pseudo first-order processes, but may have complex dependences on time (2) dispersion affects all three pollutants identically (3) dry deposition is the only type of deposition which occurs (4) deposition velocity is the same for all fine particles, but may be different for SO2 (5) secondary sulfate is produced only by homogeneous oxidation of SO2. [Pg.77]

Figure 3. First-step reactions uHth n-butenes percent olefin conversion to sulfate os. A/O ratio... Figure 3. First-step reactions uHth n-butenes percent olefin conversion to sulfate os. A/O ratio...
Derivation Condensation of benzaldehyde with die-thylaniline in presence of sulfuric acid, followed by oxidation of the triphenylmethane product formed and conversion to sulfate. [Pg.180]

Since the standard reduction potential for the SO /SO couple is +0,16 V and the standard reduction potential for the O2/H2O couple is +1,23 V then the potential difference for the equation above is = +1.23 V - 0.16 V = +1.07 V. Since this potential is large and positive, the Gibbs energy of this reaction is negative (reaction is hence spontaneous) and will be driven nearly to completion (K> 1). Thus, the expected thermodynamic fate of SO2 is its conversion to sulfate (or neutral sulfuric acid vapour). This aqueous solution of SO and H ions precipitates as acid rain, which can have a pH as low as 2 (the pH of rain water that is not contaminated with sulfuric or nitric acid is -5.6),... [Pg.62]

A model has been developed for oxidation of calcium sulfite in a three-phase, semibatch reactor, The overall rate of conversion to sulfate depends on the rates of solid dissolution and liquid phase chemical reaction. In this first treatment of the problem, gas-liquid mass transfer resistance did not affect the overall rate of oxidation. [Pg.191]

Let us take a step back and synthesize what we know about the behavior of the system and its response to an S02 emission change. A reasonable assumption for our discussion is that this local change of emissions will not affect the meteorological component of the acid deposition process (windspeed and direction, mixing, cloud occurrence and pollutant processing, rainfall, etc.). This leaves us free to concentrate on the changes of the chemical component of acid deposition. Simplifying the problem this way, we can now focus on the two components of the acid deposition—the clean-air and the cloud-related pathways. The clean-air processes include emissions of S02, atmospheric transport, conversion to sulfate by reaction with the OH radical, and dry deposition of S02 and sulfate. If we follow... [Pg.969]

Some people are sensitive to sulfur dioxide, even in trace amounts, and they can suffer severe reactions, including anaphylaxis. This is rare. Our bodies are actually used to handling sulfur dioxide, because it forms when we metabolize certain amino acids. It is usually detoxified by conversion to sulfates, which we excrete harmlessly. [Pg.90]

The insoluble salts of chloroanilic acid may be exemplified by barium chloroanilate, which is still used for the automated monitoring of sulfur dioxide emissions, after conversion to sulfate with hydrogen peroxide. Solid barium chloroanilate reacts with solutions containing sulfate to form insoluble barium sulfate, thus releasing an equivalent concentration of chloroanilic acid, which is measured by ultraviolet spectrophotometry. [Pg.111]

Although the conversion of bilirubin to glucuronide is definitely the most important pathway in the metabolism of bile pigment, conversion to sulfate is also observed to a very small extent. [Pg.388]

H2S reacting with nickel can block electrochemically active sites for the hydrogen oxidation, can change the wettability of the anode toward carbonates, can modify the anode surface and its porous structure, can alter the anode conductivity, can change the carbonate conversion to sulfate and can poison catalytic sites for the water gas shift reaction. [Pg.132]


See other pages where Conversion to sulfate is mentioned: [Pg.176]    [Pg.107]    [Pg.325]    [Pg.188]    [Pg.307]    [Pg.518]    [Pg.542]    [Pg.161]    [Pg.971]    [Pg.1052]    [Pg.1053]    [Pg.492]    [Pg.75]   
See also in sourсe #XX -- [ Pg.73 , Pg.246 ]




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