Soot particle

In pelletizing, the water—carbon slurry is contacted with a low viscosity oil which preferentially wets the soot particles and forms pellets that are screened from the water and homogenized into the oil feed to the gasification reactor (see Size enlargement). [Pg.423]

Hydrogen chloride in the lungs can cause pulmonary edema, a life threatening condition. In order for HCl in air to reach the lungs, it must be transported either as an aerosol or as a deposit on soot particles of less than 3 p.m in diameter. A procedure for the removal of 99% of the HCl from municipal waste incinerators has been developed (87). Lime is employed as a dry adsorbent which is collected in a filter bag system. [Pg.449]

The composition, properties, and size of soot particles collected from flame products vary considerably with flame conditions and growth time. Typically the C—H atomic ratio ranges from two to five and the particles consist of kregular chains or clusters of tiny spheres 10—40 nm in diameter with overall dimensions of perhaps 200 nm, although some may agglomerate further to much larger sizes. [Pg.530]

The radiation from a flame is due to radiation from burning soot particles of microscopic andsubmicroscopic dimensions, from suspended larger particles of coal, coke, or ash, and from the water vapor and carbon dioxide in the hot gaseous combustion products. The contribution of radiation emitted by the combustion process itself, so-called chemiluminescence, is relatively neghgible. Common to these problems is the effect of the shape of the emitting volume on the radiative fliix this is considered first. [Pg.578]

For Sm, Eu, and Yb, on the other hand, nanocapsules containing carbides were not found in the cathode deposit by either TEM or XRD. To see where these elements went, the soot particles deposited on the walls of the reaction chamber was investigated for Sm. XRD of the soot produced from Sm203/C composite anodes showed the presence of oxide (Sm203) and a small amount of carbide (SmC2). TEM, on the other hand, revealed that Sm oxides were naked, while Sm carbides were embedded in flocks of amorphous carbon[12J. The size of these compound particles was in a range from 10 to 50 nm. However, no polyhedral nanocapsules encaging Sm carbides were found so far. [Pg.156]

Staining or discoloration (such as to motor vehicle paint-work), as a result of acid fallout. Acid fallout is soot particles containing... [Pg.711]

The key features of soot are its chemical inertness, its physical and chemical adsorption properties, and its light absorption. The large surface area coupled with the presence of various organic functional groups allow the adsorption of many different materials onto the surfaces of the particles. This type of sorption occurs both in the aerosol phase and in the aqueous phase once particles are captured by cloud droplets. As a result, complex chemical processes occur on the surface of soot particles, and otherwise volatile species may be scavenged by the soot particles. [Pg.148]

As with conventional Cl, this is a very mild form of ionization leading to molecular species with little or no fragmentation, i.e. (M + H)+ and (M — H) . This is not, however, always the case. The use of chromatographic modifiers may change the composition of the Cl plasma to such a state that, as in Cl and thermospray, other ions may be formed, e.g. the presence of ammonium acetate may lead to (M - - NH4)+ and (M - - CHsCOO)" ions in the positive- and negative-ion modes, respectively. The chemistry of the analyte may also have an effect, as has been discussed for ESI, with, for example, the spectra of fullerenes extracted from soot particles yielding an M+ molecular species [16],... [Pg.182]

The oxidation of soot is a slow process, owing to its refractory character. Therefore, the soot particles are trapped in a filter, thus increasing the reaction time. However, catalysis is still required. The design of a catalytic filter is a challenge mainly because solid/solid contact is too poor for efficient catalysis [23]. Several ideas have been put forward. [Pg.192]

The first is to add to the diesel fuel a catalytic additive, which accumulates in the soot particles formed. The catalyst is thus brought to the right place and there is contact. [Pg.192]

One of the more significant classes of compounds resulting from and emitted by combustion sources include polycyclic aromatic hydrocarbons (PAHs) these species serve as nuclei for the formation of soot particles. Past studies have concluded that 85% of... [Pg.257]

End of Abstract Nowadays, the Diesel vehicles market in Western Europe keeps growing. Diesel technology is of interest for car manufacturers because the Greenhouse gas emissions are noticeably lower with Diesel than with gasoline (do not forget the ACEA1 commitment for 2008 140 g/km of C02 for the new cars sold in European Union). A major issue for the Diesel vehicles is to clean-up HC, CO, NO and soot particles released by the engine at a minimum cost. [Pg.212]

The evolution of Diesel standards will be discussed and the constraints and limits of Diesel after-treatment systems put in series or in development will be clarified (in particular, those dealing with NO conversion and soot particles removal). [Pg.212]

Figure 7.1. Diesel emissions standards from EuroII to EuroV on a four-axis space corresponding to the pollutants soot particles, HC, NO and CO.

The EGR system implies a NO /particle compromise. Two ways can be used to adjust the NO,/particlc compromise and allow to maintain the soot particles and NO, emission levels below the EuroIII standards ... [Pg.213]

Overall, EGR and combustion/injection systems constitute the key factors to comply with the EuroIV standards (applied in January, 2005). The EuroIV step exhibits EuroIII NO and soot particles limits divided by 2. Besides, vehicle s weight is always increasing due to the introduction of new safety systems and equipment. Therefore, pollutants emissions increase and a supplementary effort to reach the normative threshold is to be made. To comply with this target, some evolutions have been introduced, as for example multi-injection or water-cooling of the EGR system. The NO,/particle compromise adjustment remains possible for most of the applications without any after-treatment system like the Diesel particle filter (DPF). [Pg.213]

With a limit of soot particles emissions proposed at 5mg/km, the DPF has to be installed in the exhaust line and becomes mandatory for EuroV (the date of application for EuroV is unknown, of course, but foreseen in the middle of 2009). [Pg.214]

Another potential risk is the introduction of a limit value in the soot particles number (for example the limit could be fixed at 1011 particles/km). This new limitation could have a consequence on the DPF filtering medium. In such a context, the DPF technology with macro porous open medium will not be relevant any more. [Pg.217]

As illustrated on Figure 7.8, the DPF regeneration step is just a soot particles combustion reaction (soot is mainly composed by a carbon matrix), which requires a temperature in the range of 600°C and oxygen presence in the exhaust gases. [Pg.219]

Figure 7.8. DPF operating mode with alternation of soot particles trapping sequence and DPF regeneration step.

These residues are present in the exhaust gases within the soot particles and are irreversibly trapped in the DPF. They mainly consist of calcium sulfate (with other components containing zinc and iron). For the DPF technology using the fuel additivation, additives also participate in the residues formation. [Pg.220]

Do not forget that there will be a DPF in the exhaust line dedicated to the soot particles treatment and that the NO after-treatment system thus adds to the DPF. [Pg.222]

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