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Soot formation water

In a natural gas fueled PAFC, water is condensed out of the fuel stream going to the fuel cell to increase the partial pressure of hydrogen. In a coal gasification MCFC, water often is added to the fuel stream prior to the fuel cell to prevent soot formation. The addition of excess steam not only prevents the soot formation, but also causes a voltage drop of approximately 2 mV per each percentage point increase in steam content (45). The use of zinc ferrite hot gas cleanup can aggravate the soot formation problem because of the catalytic effect of the sorbent on carbon formation, and requires even higher moisture levels (46). [Pg.235]

Although the stoichiometry for reaction (9.1) suggests that one only needs 1 mol of water per mole of methane, excess steam must be used to favor the chemical equilibrium and reduce the formation of coke. Steam-to-carbon ratios of 2.5-3 are typical for natural gas feed. Carbon and soot formation in the combustion zone is an undesired reaction which leads to coke deposition on downstream tubes, causing equipment damage, pressure losses and heat transfer problems [21]. [Pg.291]

Pyrolysis. Vinyl chloride is more stable than saturated ehloroalkanes to thermal pyrolysis. That is why nearly all vmyl chlonde made commercially comes from thermal clehydrochlorination of ethylene dichloride (EDC). When vinyl chloride is heated to 450°C, only small amounts of acetylene form. Decomposition of vinyl chlonde via a free-radical chain process begins at approximately 550°C, and increases with increasing temperature. Acetylene, HC1. chloropiene, and vinylacetylene are formed in about 35% total yield at 680°C. At higher temperatures, tar and soot formation becomes increasingly important. When dry and in contact with metals, vinyl chloride does not decompose below 450°C. However, if water is present, vinyl chloride can corrode iron, steel, and alum in 11m because ofthe presence of trace amounts of HC1. This HC1 may result from the hydrolysis of the peroxide formed between oxygen and vinyl chlonde. [Pg.1683]

Contrary to expectations, small quantities of char were collected after each experiment. Soot formation was evident, and particularly prominent following the corn cob experiment. Coking of the volatile matter on the reactor wall beneath the window rendered the lower part of the reactor opaque. The water condensate was a light yellow color with a disagreeable (but not strong or particularly foul) odor. No tar was observed in the condenser, but the teflon tube connecting the reactor to the condenser was blackened. [Pg.241]

Extensive investigations at the Institute for Mechanical Engineering and Vehicle Technology at the University of Applied Science in Trier as well as practical tests showed that soot emissions were lowered by more than 90% upon the application of water-diesel micro emulsions (see Fig. 11.5(a)). Interestingly, the NO -particulate matter trade-off is avoided, i.e. nitrogen oxide emissions are also lowered significantly (Fig. 11.5(b)). The surfactants used for the formation of the microemulsion are oxidised species, which, as already mentioned above, decrease the soot formation further. [Pg.355]

Smokeless flaring is based on the principle of increasing the burning rate by the injection of steam into a flEune, by the creation of turbulence in the reacting gases and the inspiration of air, thereby reducing the formation of soot. Soot formation is also reduced by the water gas reaction, C + HgO = CO + H2, promoted by the addition of steam. [Pg.183]

Although under the conditions prevailing in the reaction zone, neither the Boudouard equilibrium nor the heterogeneous water gas reaction would justify soot formation, flee carbon is produced together with the reformed gas at a rate of O.S-2wt % in terms of the feedstock, depending on the temperature and the quantity of steam added, but also on the retention time. When the soot is recycled together with the feedstock, the soot content in the reformed gas does... [Pg.99]

For the generation of a CO-rich synthesis gas, the S/C-ratio has to be reduced because of the water-gas shift equilibrium, however, due to the risk of soot formation a minimum value, depending on the selected catalyst, must not be fallen below. Downstream the process, carbon dioxide is scrubbed out of the raw synthesis gas, which is then to be compressed and recycled to the reformer. With this scheme and the import of additional carbon dioxide, the CO-content in the synthesis gas can be further increased [5.24). [Pg.146]

The possible role of soot and water in the atmospheric oxidation of SO2 has been explored by studying the catalytic oxidation of SO2 by O2 on carbon in aqueous suspensions/ " A complex rate law was obtained, which was interpreted in terms of several equilibria involving the adsorption of O2 and S(IV) and the formation of C c 02-2S(IV), which reacts to give Q + 2S(VI). The oxidation of thiocyanate to sulfate and cyanate by alkaline hexacyanoferrate(III) with OSO4 catalyst has been discussed briefly/ ... [Pg.83]

Another field in which PAHs are molecules of interest is the study of combustion processes. In particular, the role of PAH clusters is discussed in the literature in the context of soot formation [12,13]. This field is related to environmental studies as the understanding of the nature and evolution in the atmosphere of PAHs produced by human activities or resulting from natural processes is of primary interest, due to the toxicity of these molecules. In this context, it is also important to understand the relation between PAHs and the main atmospheric compounds like water. [Pg.128]

In densely populated areas, traffic is responsible for massive exhausts of nitrous oxides, soot, polyaromatic hydrocarbons, and carbon monoxide. Traffic emissions also markedly contribute to the formation of ozone in the lower parts of the atmosphere. In large cities, fine particle exposure causes excess mortality which varies between one and five percent in the general population. Contamination of the ground water reservoirs with organic solvents has caused concern in many countries due to the persistent nature of the pollution. A total exposure assessment that takes into consideration all exposures via all routes is a relatively new concept, the significance of which is rapidly increasing. [Pg.256]

Secondly, absorbent particles such as charcoal and soot are intrinsically inert but have surfaces or infrastructures that adsorb SO, and by either coadsorption of water vapour or condensation of water within the structure, catalyse the formation of a corrosive acid electrolyte solution. Dirt with soot assists the formation of patinae on copper and its alloys by retaining soluble corrosion products long enough for them to be converted to protective, insoluble basic salts. [Pg.339]

Mercury point sources and rates of particle scavenging are key factors in atmospheric transport rates to sites of methylation and subsequent entry into the marine food chain (Rolfhus and Fitzgerald 1995). Airborne soot particles transport mercury into the marine environment either as nuclei for raindrop formation or by direct deposition on water (Rawson etal. 1995). In early 1990, both dimethylmercury and monomethylmercury were found in the subthermocline waters of the equatorial Pacific Ocean the formation of these alkylmercury species in the low oxygen zone suggests that Hg2+ is the most likely substrate (Mason and Fitzgerald 1991 Figure 5.1). [Pg.354]

Reduction of the formation of oxides of nitrogen proportionally to maintenance of water in fuel and relies on many factors. Addition of 8-25% water allows to decrease of CO emission to 40-70%, soot - to 40-60%, heavy hydrocarbons (including benzapiren) - to 70%. [Pg.48]

Both models apply the same chemical scheme of mercury transformations. It is assumed that mercury occurs in the atmosphere in two gaseous forms—gaseous elemental HgO, gaseous oxidized Hg(II) particulate oxidized Hgpart, and four aqueous forms—elemental dissolved HgO dis, mercury ion Hg2+, sulphite complex Hg(S03)2, and aggregate chloride complexes HgnClm. Physical and chemical transformations include dissolution of HgO in cloud droplets, gas-phase and aqueous-phase oxidation by ozone and chlorine, aqueous-phase formation of chloride complexes, reactions of Hg2+ reduction through the decomposition of sulphite complex, and adsorption by soot particles in droplet water. [Pg.365]


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See also in sourсe #XX -- [ Pg.287 ]




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