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Distribution of particle size

Size Distribution Relationships. Different models have been used to describe the size distribution of particles experiencing single and multiple fractures. A model based on fracture at the site of the weakest link and a distribution of weakest links in the system gave results that could be described as well by the Rosin-Rammler relation (56). The latter is based on the concept that fracture takes place at pre-existing flaws that are distributed randomly throughout the particle. [Pg.222]

Fig. 1. The size distribution of particles in an urban atmospheric dust showing the three size modes. Based on Whitby, 1977 4). Fig. 1. The size distribution of particles in an urban atmospheric dust showing the three size modes. Based on Whitby, 1977 4).
Transition-metal oxides and their mixtures are widely employed in numerous industrial applications, especially as cathode materials for batteries and fuel cells [1,2], Practice poses certain well-known requirements to oxide materials, first of all, to uniformity of the size distribution of particles, to homogeneity of mixed oxides, etc. To meet these demands, two broad categories of methods are now in use, vs (i) mechanical methods and (ii) chemical methods. [Pg.500]

As discussed in Chapter 15, the size distribution of particles in an agglomeration process is essentially determined by a population balance that depends on the kinetics of the various processes taking place simultaneously, some of which result in particle growth and some in particle degradation. In a batch process, an equilibrium condition will eventually be established with the net rates of formation and destruction of particles of each size reaching an equilibrium condition. In a continuous process, there is the additional complication that the residence time distribution of particles of each size has an important influence. [Pg.139]

The Carman-Kozeny equation relates the drop in pressure through a bed to the specific surface of the material and can therefore be used as a means of calculating S from measurements of the drop in pressure. This method is strictly only suitable for beds of uniformly packed particles and it is not a suitable method for measuring the size distribution of particles in the subsieve range. A convenient form of apparatus developed by Lea and Nurse 22 1 is shown diagrammatically in Figure 4.4. In this apparatus, air or another suitable gas flows through the bed contained in a cell (25 mm diameter, 87 mm deep), and the pressure drop is obtained from hi and the gas flowrate from h2. [Pg.203]

Size Distribution of Particles Removed. The number and size... [Pg.136]

The use of second-derivative spectra eliminated the baseline shifts observed during the reaction (which could be due to changes in the amounts or size distribution of particles, or small amounts of probe fouling). [Pg.507]

Laser diffraction is a fast alternative for analysis of the size distribution of particles in an aerosol cloud. The theory of laser diffraction is well understood [124,125]) but this technique requires special measures to test inhalation devices and to interpret the results correctly. One of the major problems is that flow adjustment through the inhaler is not possible. Furthermore, the presence of carrier particles from adhesive mixtures may disturb the measurement of the fine drug particles and the size distribution obtained is of an unknown dehvered mass fraction of the dose. These practical problems and limitations have been solved by the design of a new modular inhaler adapter for the Sympatec laser diffraction apparatus (Figure 3.6). [Pg.80]

Greenberg RR, Zoller WH, Gordon SE. 1978. Composition and size distribution of particles released in refuse incinerators. Environmental Science and Technology 12 566-573. [Pg.234]

Improved control devices now frequently installed on conventional coal-utility boilers drastically affect the quantity, chemical composition, and physical characteristics of fine-particles emitted to the atmosphere from these sources. We recently sampled fly-ash aerosols upstream and downstream from a modern lime-slurry, spray-tower system installed on a 430-Mw(e) coal utility boiler. Particulate samples were collected in situ on membrane filters and in University of Washington MKIII and MKV cascade impactors. The MKV impactor, operated at reduced pressure and with a cyclone preseparator, provided 13 discrete particle-size fractions with median diameters ranging from 0,07 to 20 pm with up to 6 of the fractions in the highly respirable submicron particle range. The concentrations of up to 35 elements and estimates of the size distributions of particles in each of the fly-ash fractions were determined by instrumental neutron activation analysis and by electron microscopy, respectively. Mechanisms of fine-particle formation and chemical enrichment in the flue-gas desulfurization system are discussed. [Pg.173]

Most readers will be familiar with the bell-shaped normal distribution plotted in Fig. 9.12. When applied to the size distribution of particles, for example, such a distribution is fully characterized by the arithmetic mean D and the standard deviation a, where a is defined such that 68% of the particles have sizes in the range D a In the log-normal distribution, the logarithm of the diameter D is assumed to have a normal distribution. (Either logarithms to the base 10 or loga-... [Pg.358]

FIGURE 9.28 Size distribution of particle geometric cross section (A) as a function of geometric diameter for a typical rural aerosol (adapted from Hegg et at., f993). [Pg.373]

FIGURE 9.33 Size distribution of particles in clouds (solid line) and below the clouds (dashed line), showing two modes (adapted from Hoppel et al., 1994). [Pg.380]

Figure 5.3. Particle size distribution of particles in figure 5.2 (a) fresh (b) after 24 hr. (After Harris et al 1983.)... Figure 5.3. Particle size distribution of particles in figure 5.2 (a) fresh (b) after 24 hr. (After Harris et al 1983.)...
The model has been used to predict the sampling efficiency of the VE for a wide range of MMAD and GSD values typical of what might be encountered in cotton textile processing. These parameter values are for the actual size distribution of particles in the sampled air, and not for those collected on the membrane filter. These results are summarized in Table II. A remarkable feature of this model is that it predicts that the VE will collect significant amounts of particles with aerodynamic diameters greater than 30 pm. [Pg.68]

Particle Measurements. A variety of instruments is available for measuring the number density and size distribution of particles sampled from airborne platforms. This discussion is restricted to instruments that measure particles smaller than 50 xm (cloud droplets and aerosol particles) because these particles are of most interest to atmospheric chemists. [Pg.136]

Static Electrification of Dust Particles. Kunkel (l Y) has made an extensive study of the charge and size distribution of particles ranging from 0.5- to 30-micron radius in dust clouds in air and has investigated both calm and turbulent conditions. [Pg.149]

Deposition doses in the human respiratory system were estimated based on the roadside PNCs in various locations. These showed the similar trend to the roadside PNCs since the dose estimates did not take into account the size distributions of particles at each site. Average deposition doses over all the considered locations were found to be 3.61 0.17 x 1010 h 1 for male subjects, with exceptionally high values (1.61 0.08 x 1011 h ) for site at Birmingham where the study was carried out along the roadside about 15 years ago (i.e. in 1996-1997). [Pg.359]

Saltikov SA (1967) The determination of the size distribution of particles in an opaque material from a measurement of the size distribution of their sections. In Stereology. Elias H (ed) Springer-Verlag, New York, p 163-173... [Pg.214]

In the simulation mns, the design parameters were chosen as d = (u,D), i.e. the kinetic parameters of breakage and the classification function were fixed. The size distribution of particles in the feed stream was constant, selecting 0 for x = xmax/2 and 0.05 for x > xmax/2, while the initial size distribution of the material in the mill was the same in each run. The largest particle size was chosen xmax = 10-3 m, and the values of the kinetic parameters were Ks = 10-4, a = 1.00, /3 = 3.00, y = 0.60,

classification function jump function of the form... [Pg.275]


See other pages where Distribution of particle size is mentioned: [Pg.126]    [Pg.1827]    [Pg.297]    [Pg.168]    [Pg.81]    [Pg.773]    [Pg.193]    [Pg.11]    [Pg.23]    [Pg.675]    [Pg.376]    [Pg.94]    [Pg.94]    [Pg.94]    [Pg.563]    [Pg.145]    [Pg.347]    [Pg.52]    [Pg.53]    [Pg.49]    [Pg.405]    [Pg.50]    [Pg.84]    [Pg.107]    [Pg.74]    [Pg.136]    [Pg.159]    [Pg.48]   
See also in sourсe #XX -- [ Pg.69 ]




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