Capacity comparison fractionator

Fractionation efficiency, 6,11,195-196, 209, 365 fractionator problems, 195-196, 209 Fractionator problems (FCCU product fractionation), 18f3-200 flooding, 188-189 load observation, 189-191 liquid loading sensitivity, 189 capacity comparison, 189,192-193 heattransfer coefficients, 193-194 structured packing heat transfer, 193 height equivalent to theoretical stage,... 

Table 6.6. Comparisons of the redistribution of metals in two Israeli soils at 3T treatment. Soils were incubated for one year under the saturated paste (SP), field capacity (FC) and wetting-drying cycle (Cycle) moisture regimes (% of the sum of fractions, as means of two replicates) (from Han et al., 2001a, with permission from Lippincott Williams Wilkins)...

Figure 10.83 Comparison between calculated and experimental (Fincham and Richardson 1954, 1964, Sharma and Richardson 1965) sulphide capacities in A0-Si02-Al203 slags (where A=Mn, Mg, Ca) at a constant SiOj fraction of...

Fig. 28. Validation of the NSRC model for passenger car application—comparison of measured (meas) and calculated (calc) cumulative NOx emissions for the FTP-75 driving cycle fresh catalyst (Giithenke et al., 2007a). The covered fraction of the NOx storage capacity (spatially averaged i//N( )x) is calculated by the model. Integral NOx conversions X evaluated from experiment and simulation data Xexp = 88.9%, Tslm = 88.3% (see Plate 5 in Color Plate Section at the end of this book).

Then, a comparison of complex formation constants which are tackled in the colloquial manner affords a numerical value which corresponds to an average fractionation capacity of that mixture or biomass sample with respect to metal ions. Yet the scope is broader toxicity issues in comparison of various heavy metals or other biochemical properties such as biocatalytic efficiency can be addressed in the same way as simple accumulation or fractionation (including the fact that fractionation may be amplified relative to differences of complex stabihties by multiple speciation events or by transmembrane transports). 

Except for the humic acid fraction (130 mg g TOC), all maximum measured adsorption capacities are low ( 50 mg g TOC) in comparison with most other organics moreover the adsorption isotherms are very steep (Figs. 2—6). 

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