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Sulfur aerosol size distribution

Based on the use of the NARCM regional model of climate and formation of the field of concentration and size distribution of aerosol, Munoz-Alpizar et al. (2003) calculated the transport, diffusion, and deposition of sulfate aerosol using an approximate model of the processes of sulfur oxidation that does not take the chemical processes in urban air into account. However, the 3-D evolution of microphysical and optical characteristics of aerosol was discussed in detail. The results of numerical modeling were compared with observational data near the surface and in the free troposphere carried out on March 2, 4, and 14, 1997. Analysis of the time series of observations at the airport in Mexico City revealed low values of visibility in the morning due to the small thickness of the ABL, and the subsequent improvement of visibility as ABL thickness increased. Estimates of visibility revealed its strong dependence on wind direction and aerosol size distribution. Calculations have shown that increased detail in size distribution presentation promotes a more reliable simulation of the coagulation processes and a more realistic size distribution characterized by the presence of the accumulation mode of aerosol with the size of particles 0.3 pm. In this case, the results of visibility calculations become more reliable, too. [Pg.46]

It is therefore mainly limited to the cocondensation of sulfuric acid and water. The acid in this case is produced in the atmosphere by gas phase oxidation of SO2. A special case is the production of sea salt aerosols over the oceans, which are effectively produced by the disintegration of air bubbles on the ocean. The atmospheric aerosol is a dynamic system the initially produced particles undergo various processes like heterogeneous condensation, coagulation, and deposition which lead to a change in their size and chemical composition and gives rise to the universality of the aerosol size-distribution. [Pg.242]

Hering, S. V., and S. K. Friedlander, Origins of Aerosol Sulfur Size Distributions in the Los Angeles Basin, Atmos. Environ 11 2647-2656 (1982). [Pg.399]

On the average, the requirements for application of the statistical technique to filter data were met. Analysis of the 254 measured particle size distributions in 1979 indicates that the fine aerosol volume distribution preserved its shape. The measured sulfur mass distribution followed that of the total submicron volume. By difference, it was assumed that the organics did the same. The low relative humidity at China Lake minimized the formation of aqueous solutions due to water condensation on the particles. Therefore, it is expected that the statistical technique can be used with some success with the China Lake filter data. [Pg.144]

It was found that the requirements were satisfied for application of the linear regression technique to species mass concentrations in a multicomponent aerosol. The results of 254 particle size distributions measured at China Lake in 1979 indicate that the normalized fine aerosol volume distribution remained approximately constant. The agreement between the calculated and measrued fine particle scattering coefficients was excellent. The measured aerosol sulfur mass distribution usually followed the total distribution for particles less than 1 ym. It was assumed that organic aerosol also followed the total submicron distribution. [Pg.152]

Sievering, H., J. Boatman, J. Galloway, W. Keene, Y. Kim, M. Luria, and J. Ray, Heterogeneous Sulfur Conversion in Sea-Salt Aerosol Particles The Role of Aerosol Water Content and Size Distribution, Atmos. Environ., 25A, 1479-1487 (1991). [Pg.346]

On-line measurements of the sulfur content of atmospheric aerosols have been made by removing gaseous sulfur species from the aerosol and then analyzing the particles for sulfur with a flame photometric detector (24) or by using an electrostatic precipitator to chop the aerosol particles from the gas so that the sulfur content could be measured by the difference in flame photometric detector response with and without particles present. These and similar methods could be extended to the analysis of size-classified samples to provide on-line size-resolved aerosol composition data, although the analytical methods would have to be extremely sensitive to achieve the size resolution possible in size distribution analysis. [Pg.205]

Figure 7. Sulfur size distributions at Grand Canyon National Parky August 1984, The finest aerosols are at the top (stage 8, around 0.1 xm), and the coarsest (8.5 to about 15 xm) are at the bottom. Most sulfur mass occurs between 0.34 and 0.56 xm (stage 6). The periods of August 14 are used for Table 111. (Reproduced with permission from reference 15. Copyright 1988.)... Figure 7. Sulfur size distributions at Grand Canyon National Parky August 1984, The finest aerosols are at the top (stage 8, around 0.1 xm), and the coarsest (8.5 to about 15 xm) are at the bottom. Most sulfur mass occurs between 0.34 and 0.56 xm (stage 6). The periods of August 14 are used for Table 111. (Reproduced with permission from reference 15. Copyright 1988.)...
Sulfate aerosols are important for cloud processes and climate because they act, like sea salt aerosol, as CCN. The total number and size distribution of CCN determine the microphysical and, therefore, also radiative properties of clouds. In Section 4.02.4.4 we already discussed the possible involvement of iodine in seeding the formation of sulfate CCN. DMS is the most important precursor for SO2 and sulfate aerosol in the remote MBL. A possible link between iodine and sulfur chemistry was investigated by Chatfield and Crutzen (1990), using a reaction rate coefficient of the lO -p DMS reaction available at that time. They concluded that at that rate this reaction could play a significant role for the oxidation of DMS. In an alternative scenario with a slower rate coefficient, they found the iodine and sulfur cycles to be decoupled, in better agreement with field observations. Later the reaction turned out to be even slower than their lower limit (DeMore et al., 1997 Knight and Crowley, 2001). [Pg.1960]

In the quadrature method of moments (QMOM) developed by McGraw [131], for the description of sulfuric acid-water aerosol dynamics (growth), a certain type of quadrature function approximations are introduced to approximate the evolution of the integrals determining the moments. Marchisio et al [122, 123] extended the QMOM for the application to aggregation-breakage processes. For the solution of crystallization and precipitation kernels the size distribution function is expressed using an expansion in delta functions [122, 123] ... [Pg.1080]

An important example related lo the atmospheric aerosol is the droplet containing dissolved sulfates that form as a result of the oxidation of SO2 in solution. The sulfates may be present a.s sulfuric acid or in a partially neutralized form as ammonium salts or metallic salts from sources such as flyash. The droplet size distribution and chemical composition are determined by a combination of thermodynamic and rate processes. In this section, we consider only equilibrium thermodynamics as it affects the vapor pressure of the drop. [Pg.255]

In the fourth type of identification the chemical composition of particles is studied in situ. By suitable chemical aerosol instruments the concentration and the size distribution of certain elements can be continuously monitored. The flame photometry of sodium containing particles (e.g. Hobbs, 1971) is a good example for such a method. Recently flame photometric detectors have also been developed to measure aerosol sulfur in the atmosphere (e.g. Kittelson et at., 1978). [Pg.114]

Fig.2.3. Moments of particle size distribution for nucleation and growth of sulfuric acid aerosol from sulfuric acid vapor at low humidity. Number concentration, cm , x 2E5, 0 mass concentration, g/ccxlE-13, + surface, cm xlE-7, 1/Number, cm ... Fig.2.3. Moments of particle size distribution for nucleation and growth of sulfuric acid aerosol from sulfuric acid vapor at low humidity. Number concentration, cm , x 2E5, 0 mass concentration, g/ccxlE-13, + surface, cm xlE-7, 1/Number, cm ...
Continental aerosol particles contain a significant fraction of minerals. The insoluble fraction consists mainly of the major crustal elements silicon, aluminum and trivalent iron, which occur as alumino-silicates, quartz, and iron oxides. Elements that are eluted from minerals by water are sodium, potassium, calcium (inpart), and magnesium. The water-soluble inorganic salt ftaction is dominated by am-monimn sulfate. Again, sulfate arises from the oxidation of sulfur dioxide, both by gas-phase and by aqueous phase reactions. Whereas the mineral components are mainly found in the coarse particle size range, ammonium sulfate resides mainly in the accumulation mode. Nitrate occurs partly in association with ammoniirm in the accumulation mode, and partly together with sodiirm and other cations in the coarse particle mode. Thus, nitrate often shows a bimodal size distribution. [Pg.360]

Hering, S.V., Friedlander, S.K. (1982). Origins of aerosol sulfur size distributions in the Los Angeles basin. Atmos. Environ. 11, 2647-2656. [Pg.56]

Chu et al. (1987) present results of laboratory studies of the formation of an ultrafine aerosol by converting SO- to sulfuric acid using measurement methods described by Holub and Knutson (1987) and Kulju et al. (1987). It was found that the size of the resulting activity distributions is dependent on the S02 concentration. The role of humidity is still unclear and more studies are needed, but it appears that both future theoretical models and laboratory studies will be extremely fruitful in elucidating the behavior of Po-218 from shortly after its formation until its incorporation into the existing accumulation mode aerosol. [Pg.10]

Pollutant. A pollutant can be defined"as a substance that is brought near a receptor by the atmosphere. A particular pollutant is distinguished from others by its physical and chemical properties. For example, it may be a gas or it may be an aerosol with a certain distribution of particle sizes oxides of sulfur may be present as S02, S03, or H2S04. The pollutant can also be characterized with respect to concentration, the length of time that a certain concentration is present, or the frequency distributions of periods of known duration and concentration (1). The pollutant... [Pg.60]

Several methods were used to characterize aerosol distributions within the exposure chambers. The principal method employed a rectangular jet impactor which was inserted through a port in the chamber and used to inertially classify particles larger than 0.3 urn in diameter. As an additional index, total sulfuric acid mass use per total mass flow was calculated to give an approximation of H SO, mass per volume. Since a substantial part of the aerosol distribution in this system was below inertial impaction limits, an electrical mobility size analyzer (Thermo-... [Pg.278]


See other pages where Sulfur aerosol size distribution is mentioned: [Pg.141]    [Pg.348]    [Pg.1179]    [Pg.488]    [Pg.393]    [Pg.125]    [Pg.178]    [Pg.206]    [Pg.22]    [Pg.432]    [Pg.2037]    [Pg.280]    [Pg.374]    [Pg.43]    [Pg.123]    [Pg.333]    [Pg.336]    [Pg.16]    [Pg.203]    [Pg.1897]    [Pg.932]    [Pg.586]    [Pg.205]    [Pg.223]   
See also in sourсe #XX -- [ Pg.223 , Pg.225 ]




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