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Surface load

Pressure filters are worth noting. These are usually set up in the form of steel cylinders positioned vertically. Another variation consists of using horizontal filtration groups. This has the drawback that the surface loading is variable in the different layers of the filter bed moreover, it increases with greater penetration in the filter bed (the infiltration velocity is lowest at the level of the horizontal diameter of the cylinder). The filter bottom usually consists of a number of screens or mesh sieves that decrease in size from top to bottom or, as an alternative, perforated plates supporting gravel similar to that used in the filter bottoms of an open filter system. [Pg.258]

ORR catalysis by Fe or Co porphyrins in Nation [Shi and Anson, 1990 Anson et al., 1985 Buttry and Anson, 1984], polyp5rrolidone [Wan et al., 1984], a surfactant [Shi et al., 1995] or lipid films [CoUman and Boulatov, 2002] on electrode surfaces has been studied. The major advantages of diluting a metalloporphyrin in an inert film include the abUity to study the catalytic properties of isolated molecules and the potentially higher surface loading of the catalyst without mass transport Umit-ations. StabUity of catalysts may also improve upon incorporating them into a polymer. However, this setup requires that the catalyst have a reasonable mobUity in the matrix, and/or that a mobile electron carrier be incorporated in the film [Andrieux and Saveant, 1992]. The latter limits the accessible electrochemical potentials to that of the electron carrier. [Pg.652]

It should be noted that in all cases the size (and hence cost) of end-of-pipe treatment has a direct relationship to both the volume of effluent to be treated and the concentration of pollutants contained in the discharge. For example, the size of most physicochemical reactors (balancing, neutralizing, flocculation, sedimentation, flotation, oxidation, reduction, etc.) is determined by hydraulic factors such as surface loading rate and retention time. [Pg.2]

Preliminary research has shown that Brillouin fiber-optic sensing systems provide a possible method to detect leaks and third-party intrusion on a pipeline over distances of 25 km or more. Their intrinsic response to both temperature and mechanical strain allows for the separation of these parameters and the detection of anomalies in the scan profiles. In addition, the same sensor could be integrated into the pipeline system to detect possible ground movement relative to fixed reference points. Limited test results on surface loads associated with the intrusion of vehicles and people on a pipeline have demonstrated the sensitivity of the system and its ability to discriminate loads at different soil depths. [Pg.366]

Uptake measurements were made [16] at several oxide/solution ratios, reported as surface loading (SL) or m2 oxide surface/liter of solution, as PdCl, 2 concentration was increased and pH was held constant at the optimal value (Figure 6.10a). Each SL indeed indicated a plateau near the steric value [16], For Pt and Pd ammine cations, the maximum surface density over many oxides appears to be a close-packed layer, which retains two hydration sheaths representative results for PTA uptake over silica from a recent paper [19] are shown in Figure 6.10b. The physical limit of cationic ammine surface density thus appears to be 0.84 pmol/m2, or about 1 cationic complex/2 nm2. Cationic uptake, therefore, is inherently half of anion uptake in many cases. [Pg.168]

Figure 6.15 pH shift measurements and the pH shift portion of the RPA model at various surface loadings for a typical y-alumina. (From Regalbuto, J.R., Navada, A., Shadid, S., Bricker, M.L., and Chen, Q., J. Catal. 184, 1999, 335.)... [Pg.175]

References Pt Loading (wt %) Surface Area (m2/g) Surface Loading ( imol/m2) Method... [Pg.180]

Figure 6.22 A PTA-pH survey for a surface loading of 83,000 m2/L. The solutions were basified with either NaOH (diamonds) or NH4OH (squares). (From Miller, J.T., Schreier, M., Kropf, A.J., and Regalbuto, J.R., J. Catal. 225, 2004, 203.)... Figure 6.22 A PTA-pH survey for a surface loading of 83,000 m2/L. The solutions were basified with either NaOH (diamonds) or NH4OH (squares). (From Miller, J.T., Schreier, M., Kropf, A.J., and Regalbuto, J.R., J. Catal. 225, 2004, 203.)...
The Equilibrium pH of activated carbon at various surface loadings... [Pg.186]

Calculate the surface loading at incipient wetness for the following cases ... [Pg.192]

Figure 8.2. Fluorescence emission and excitation spectra of a strongly scattering sample as detected in forward (Ff) and backward (Fb) direction. (Pyrene adsorbed on silica gel, surface loading cpyr = 5.5-10-7 mol g l, spec, surface area cisiiica = 500 m2 g ),... Figure 8.2. Fluorescence emission and excitation spectra of a strongly scattering sample as detected in forward (Ff) and backward (Fb) direction. (Pyrene adsorbed on silica gel, surface loading cpyr = 5.5-10-7 mol g l, spec, surface area cisiiica = 500 m2 g ),...
Figure 8.8. Examples of nonexponential fluorescence decay curves 9,10-diphenyl-anthracene on alumina for chromatographic purposes (Uhl.Oelkrug, unpublished results) (unnumbered curves time profiles of the excitation pulse, 2 - 360 nm). Upper left effect of environment (1) high vacuum, (2) liquid n-hexane. c=3/tmol g"1,2 =440 nm. Upper right effect of fluorescence wavelength (1) 2 = 500 nm, (2) 440 nm, (3) 406 nm c=3 /tmol g 1. Lower left effect of surface loading (1) 3 /rmol g (2) 0.13 mol g , (3) 0.02/r mol g"1 2e=440. Lower right effect of sample thickness (l) d - . (2) d - 0 c - 3 /tmol g 1, 2 = 440 nm. Figure 8.8. Examples of nonexponential fluorescence decay curves 9,10-diphenyl-anthracene on alumina for chromatographic purposes (Uhl.Oelkrug, unpublished results) (unnumbered curves time profiles of the excitation pulse, 2 - 360 nm). Upper left effect of environment (1) high vacuum, (2) liquid n-hexane. c=3/tmol g"1,2 =440 nm. Upper right effect of fluorescence wavelength (1) 2 = 500 nm, (2) 440 nm, (3) 406 nm c=3 /tmol g 1. Lower left effect of surface loading (1) 3 /rmol g (2) 0.13 mol g , (3) 0.02/r mol g"1 2e=440. Lower right effect of sample thickness (l) d - . (2) d - 0 c - 3 /tmol g 1, 2 = 440 nm.
Figure 8. Configurations for plasma etch reactors, (a) barrel or volume loaded 0)) parallel plate or surface loaded (c) downstream etcher. Figure 8. Configurations for plasma etch reactors, (a) barrel or volume loaded 0)) parallel plate or surface loaded (c) downstream etcher.
Figure 3.3 Oligonucleotide probe surface loading vs. hybridization efficiency. (From Zammatteo, N. et al.. Anal. Biochem., 280, 143-150, 2000. With permission.)... Figure 3.3 Oligonucleotide probe surface loading vs. hybridization efficiency. (From Zammatteo, N. et al.. Anal. Biochem., 280, 143-150, 2000. With permission.)...
The USEPA surveys identified four resin adsorption systems in the pesticide industry [7]. Phenol, pesticide, and diene compounds are all effectively removed by these systems. At least one system realized a significant product recovery via regeneration and distillation. The design surface loading rates vary from 1.0 to 4.0 gpm/ft with empty bed contact times of 7.5 to 30 minutes. [Pg.531]

Figure 3.2 Signal patterns from 80% organic vapor samples at 120°C. Responses are normalized to the surface loading of ionic liquids and the concentrations of vapors in the carrier gas. (Reprinted from Jin, X., Yu, L., Garcia, D., Ren, R.X., and Zeng, X., Anal. Chem., 78,6980-6989,2006. Copyright 2006 American Chemical Society. With permission.)... Figure 3.2 Signal patterns from 80% organic vapor samples at 120°C. Responses are normalized to the surface loading of ionic liquids and the concentrations of vapors in the carrier gas. (Reprinted from Jin, X., Yu, L., Garcia, D., Ren, R.X., and Zeng, X., Anal. Chem., 78,6980-6989,2006. Copyright 2006 American Chemical Society. With permission.)...
The emphasis in the present work is on leachates derived from fly ash disposal, but it must not be forgotten that fine ash particles may escape from power plants. The transport and dispersion of particulate emissions from tall stacks has been actively researched over the last 20-30 years. A review by Carras (1995) records that plumes have been observed to remain as coherent units up to distances of at least 1800 km and thus deposit pollution far from source. However, maximum particulate surface loadings are likely to be found adjacent to old power plants with limited fine-particle fly ash entrapment. Evans et al. (1980) estimated that in a period of 23 years the cumulative stack ash load at a distance of 1.7 km from an 83 MW... [Pg.621]

Table 7.1 shows that rather similar results were also found by Makri et al. (2005) for samples of coarse emulsions containing thermodynamically incompatible mixtures of legume seed protein + xanthan gum. The protein surface load was found to be enhanced in the presence of xanthan gum, especially at elevated ionic strengths. That is, there was observed to be an increase in the adsorption of legume seed proteins at the surface of the emulsion droplets which could be attributed to an increase in the thermodynamic activity of the proteins in the system in the presence of the incompatible polysaccharide (see Table 7.1). Associated with the greater extent of protein adsorption, the authors reported an enhancement in the emulsion stability. Table 7.1 shows that rather similar results were also found by Makri et al. (2005) for samples of coarse emulsions containing thermodynamically incompatible mixtures of legume seed protein + xanthan gum. The protein surface load was found to be enhanced in the presence of xanthan gum, especially at elevated ionic strengths. That is, there was observed to be an increase in the adsorption of legume seed proteins at the surface of the emulsion droplets which could be attributed to an increase in the thermodynamic activity of the proteins in the system in the presence of the incompatible polysaccharide (see Table 7.1). Associated with the greater extent of protein adsorption, the authors reported an enhancement in the emulsion stability.
Fig. 4.3.19. Indents on steel surface. Loads 2943, 1962, 981, 490, 245 and 147 mN, scale graduation = 25 fxm, magnification 540 x. (After Leitz-Wetzlar)... Fig. 4.3.19. Indents on steel surface. Loads 2943, 1962, 981, 490, 245 and 147 mN, scale graduation = 25 fxm, magnification 540 x. (After Leitz-Wetzlar)...
Figure 7. Configuration for plasma etch and deposition reactors, (a) parallel-plate or surface-loaded design with wafers positioned horizontally (h) parallel-plate design with vertical electrodes with a furnace tube (c) external coupling, downstream (d) external coupling, (a Reproduced from reference 2. Copyright 1983 American Chemical Society, b-d Reproduced with permission from reference 46. Copyright 1983 American Society for Testing and Materials.)... Figure 7. Configuration for plasma etch and deposition reactors, (a) parallel-plate or surface-loaded design with wafers positioned horizontally (h) parallel-plate design with vertical electrodes with a furnace tube (c) external coupling, downstream (d) external coupling, (a Reproduced from reference 2. Copyright 1983 American Chemical Society, b-d Reproduced with permission from reference 46. Copyright 1983 American Society for Testing and Materials.)...

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See also in sourсe #XX -- [ Pg.308 ]

See also in sourсe #XX -- [ Pg.120 ]




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