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Composite sorption

The case study showed a successful method for manufacturing composite sorption materials for ion removal by electrosorption. The prepared electrosorption membranes that were electrochemically activated at 10 V and removed approximately 100% of Ni and >90% of Na" ", S04, and CP ions from a simulated nickel effluent solution. The energy consumption at... [Pg.1081]

Distributed Reactivity Model. Isotherm relationships observed for natural systems may well be expected to reflect composite sorption behavior resulting from a series of different local isotherms, including linear and nonlinear adsorption reactions. For example, an observed near-linear isotherm might result from a series of linear and near-linear local sorption isotherms on m different components of soft soil organic matter and p different mineral matter surfaces. The resulting series of sorption reactions, because they are nearly linear, can be approximated in terms of a bulk linear partition coefficient, KDr that is... [Pg.373]

Composite Sorption Magnitude and Isotherm Nonlinearity. Accurate assessment of the extent to which the global isotherm for a system is nonlinear is important for accurate portrayal of sorption processes in that system. From a practical point of view, the extrapolation of linear approximations of weakly nonlinear or near-linear sorption isotherms to concentration ranges beyond which they are valid can result in significant errors in projections of contaminant fate and transport (1). From a conceptual point of view, observations of isotherm nonlinearity over specific concentration ranges may be employed in conjunction with models such as the DRM to probe and evaluate the extent to which multiple sorption mechanisms are operative in a particular system. [Pg.375]

The experimental results given in Figure 7 provide confirmation of the importance of such small but highly reactive nonlinearly sorbing components to the overall sorption behavior of hydrophobic contaminants in subsurface systems. This figure presents a comparison of the carbon-normalized contribution of the nonlinear local TCB isotherm for the shale isolated from the Wagner soil to the composite sorption isotherm for the soil itself. [Pg.376]

In the preceding chapter it had already been discussed that it is less the synthesis itself which may be the bottleneck in high-throughput zeolite science but rather the analysis of the solids formed in a high-throughput program. There are several standard characterization techniques which are typically employed to characterize zeolitic materials. These include powder XRD for phase identification, X-ray fluorescence analysis (XRF) or atomic absorption spectrometry to analyze elemental composition, sorption analysis to study the pore system, IR-speclroscopy, typically using adsorbed probe molecules to characterize the acid sites, NMR spectroscopy and many others. For some of these techniques parallelized solutions have been developed and described in the literature, other properties are more difficult to assess in a parallelized or even a fast sequential fashion. [Pg.166]

Correlation coefficients calculated in a similar manner for multiple pairings of radioelements can be included as input into the PA sampling routine, allowing the value selected for one radioelement sorption parameter to be conditioned by its geochemical relationship to the other radioelements. Theoretically, for a given water composition, sorption coefficients of two or more radioelements should be determinate based on the geochemical controls on their. sorption behavior. In this sense, the soiplion c )ellicienls are deterministically correlated, rhe.se ty XJs of cor-... [Pg.227]

Effect of size of AMP-PUF on Cs" sorption. To elucidate the above, AMP-PUF was milled and sieved to fragmentize by size. Effect of the size on sorption kinetics of Cs was studied for 10 mL solution containing 500 pg of Cs. Fig. 4 shows the results by decreasing the size of the composite, sorption kinetics was effectively improved. Comparison of the results between milled fragments and 5 mm cube suggests that sorption kinetics is considerably improved by increase in an effective surface area of the composite and will be strongly influenced by osmotic behavior of solution into PUF. [Pg.116]

Fig. 3. Effects of composition on physical properties. A, acetyl B, butyryl C, cellulose. 1, increased tensile strength, stiffness 2, decreased moisture sorption 3, increased melting point 4, increased plasticizer compatibiUty 5, increased solubiUties in polar solvents 6, increased solubiUties in nonpolar... Fig. 3. Effects of composition on physical properties. A, acetyl B, butyryl C, cellulose. 1, increased tensile strength, stiffness 2, decreased moisture sorption 3, increased melting point 4, increased plasticizer compatibiUty 5, increased solubiUties in polar solvents 6, increased solubiUties in nonpolar...
Sorption activity differences of listed elements on aerosile A-300 and K-7-30 have been established depending from pH media. It was marked that disparity of pH sorption optimum values (pH, ) is caused by changes of composition and stmcture of hydrated cover ot sorbents. The presence of hydrated and a solvate surface layer on K-7-30 is the reason of differences at degree of hydrolysis of taken elements and composition of their hydrolyzed forms. [Pg.265]

PSS-SG composite film was tested for sorption of heme proteins hemoglobin (Hb) and myoglobin (Mb). The peroxidaze activity of adsorbed proteins were studied and evaluated by optical and voltammetric methods. Mb-PSS-SG film on PG electrode was shown to be perspective for detection of dissolved oxygen and hydrogen peroxide by voltammetry with linear calibration in the range 2-30 p.M, and detection limit -1.5 p.M. Obtained composite films can be modified by different types of biological active compounds which is important for the development of sensitive elements of biosensors. [Pg.306]

SG sols were synthesized by hydrolysis of tetraethyloxysilane in the presence of polyelectrolyte and surfactant. Poly (vinylsulfonic acid) (PVSA) or poly (styrenesulfonic acid) (PSSA) were used as cation exchangers, Tween-20 or Triton X-100 were used as non- ionic surfactants. Obtained sol was dropped onto the surface of glass slide and dried over night. Template extraction from the composite film was performed in water- ethanol medium. The ion-exchange properties of the films were studied spectrophotometrically using adsorption of cationic dye Rhodamine 6G or Fe(Phen) and potentiometrically by sorption of protons. [Pg.317]

Scott and Kucera [4] carried out some experiments that were designed to confirm that the two types of solute/stationary phase interaction, sorption and displacement, did, in fact, occur in chromatographic systems. They dispersed about 10 g of silica gel in a solvent mixture made up of 0.35 %w/v of ethyl acetate in n-heptane. It is seen from the adsorption isotherms shown in Figure 8 that at an ethyl acetate concentration of 0.35%w/v more than 95% of the first layer of ethyl acetate has been formed on the silica gel. In addition, at this solvent composition, very little of the second layer was formed. Consequently, this concentration was chosen to ensure that if significant amounts of ethyl acetate were displaced by the solute, it would be derived from the first layer on the silica and not the less strongly held second layer. [Pg.102]

Due to the chemical structure, fimctionality and composition of their constituents, ordinary variations of the processing conditions as well as the quality of the raw materials have been observed to lead to changes of the fine structure which are often responsible of lower ageing resistence of the polymer. The data reported here correlate the morphology of some widely utilized epoxy matrices to the informations that can be obtained from the study of the sorption behaviours. [Pg.189]

In order to evaluate the effect of hygrothermal fatigue on the physical and mechanical properties of composites in actual service, it is crucial to resolve the basic phenomena driving the complex water sorption behaviour and degradation mechanisms in various combinations of moist environment and temperature. [Pg.191]


See other pages where Composite sorption is mentioned: [Pg.130]    [Pg.372]    [Pg.381]    [Pg.579]    [Pg.580]    [Pg.376]    [Pg.385]    [Pg.130]    [Pg.372]    [Pg.381]    [Pg.579]    [Pg.580]    [Pg.376]    [Pg.385]    [Pg.271]    [Pg.272]    [Pg.33]    [Pg.199]    [Pg.1540]    [Pg.107]    [Pg.304]    [Pg.440]    [Pg.104]    [Pg.141]    [Pg.47]    [Pg.284]    [Pg.43]    [Pg.10]    [Pg.271]    [Pg.431]    [Pg.192]    [Pg.198]    [Pg.200]   
See also in sourсe #XX -- [ Pg.372 , Pg.373 , Pg.374 ]

See also in sourсe #XX -- [ Pg.372 , Pg.373 , Pg.374 ]




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