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Water ADSORPTION

The electrochemical environment also contained water vapor from the electrolyte solution. In UHV studies no water adsorption was found at room temperature on clean or CO-covered Ni(lll) surface at a dosage of about 20 L, in agreement with the generally accepted understanding of water/nickel interactions.  [Pg.118]

C0-c(4x2)/Ni(lll) surfaces transferred to the electrochemical chamber under UKV, left there for about 30 minutes (the time [Pg.118]

CO unprotected Ni(lll) surfaces yielded after the same procedure a TPD-CO peak corresponding to ca. 5% of the amount observed for a CO-c(4x2)/Ni(lll). This level of CO contamination was also observed even for a sample left in the main chamber for 30 minutes and may be regarded as noimial for typical UHV systems with partial pressures of CO of about 1 x 10 torr. [Pg.119]

Transfer experiments similar to chose described above were also performed with bare Ni(lll) surfaces. After being exposed to che moist 1 atm. Ar in the presence of the electrochemical cell [Pg.119]


There are complexities. The wetting of carbon blacks is very dependent on the degree of surface oxidation Healey et al. [19] found that q mm in water varied with the fraction of hydrophilic sites as determined by water adsorption isotherms. In the case of oxides such as Ti02 and Si02, can vary considerably with pretreatment and with the specific surface area [17, 20, 21]. Morimoto and co-workers report a considerable variation in q mm of ZnO with the degree of heat treatment (see Ref. 22). [Pg.349]

Cortona embedded a DFT calculation in an orbital-free DFT background for ionic crystals [183], which necessitates evaluation of kinetic energy density fiinctionals (KEDFs). Wesolowski and Warshel [184] had similar ideas to Cortona, except they used a frozen density background to examine a solute in solution and examined the effect of varying the KEDF. Stefanovich and Truong also implemented Cortona s method with a frozen density background and applied it to, for example, water adsorption on NaCl(OOl) [185]. [Pg.2226]

Abstract. A model of the conformational transitions of the nucleic acid molecule during the water adsorption-desorption cycle is proposed. The nucleic acid-water system is considered as an open system. The model describes the transitions between three main conformations of wet nucleic acid samples A-, B- and unordered forms. The analysis of kinetic equations shows the non-trivial bifurcation behaviour of the system which leads to the multistability. This fact allows one to explain the hysteresis phenomena observed experimentally in the nucleic acid-water system. The problem of self-organization in the nucleic acid-water system is of great importance for revealing physical mechanisms of the functioning of nucleic acids and for many specific practical fields. [Pg.116]

Taking into account the hydration shell of the NA and the possibility of the water content changing we are forced to consider the water -I- nucleic acid as an open system. In the present study a phenomenological model taking into account the interdependence of hydration and the NA conformation transition processes is offered. In accordance with the algorithm described above we consider two types of the basic processes in the system and thus two time intervals the water adsorption and the conformational transitions of the NA, times of the conformational transitions being much more greater... [Pg.117]

The problem of the theoretical description of biopolymer water adsorption isotherms has drawn the attention of researchers for a long time. In the works [19], [20] a rigorous statistical basis for equations describing the isotherms for the case of homogeneous adsorption surfaces and noninteracting adsorption sites of N different types has been suggested. The general equation is ... [Pg.120]

Fig. 5.12 (a) Water adsorption isotherms at 20°C on Graphon activated to 24-9 % burn-off, where its active surface was covered to varying extents by oxygen complex. (b) The results of (a) plotted as amount adsorbed per of active surface area (left-hand scale) and also as number of molecules of water per atom of chemisorbed oxygen (right-hand scale). (After Walker.)... [Pg.265]

This principle is illustrated in Figure 10 (45). Water adsorption at low pressures is markedly reduced on a poly(vinyhdene chloride)-based activated carbon after removal of surface oxygenated groups by degassing at 1000°C. Following this treatment, water adsorption is dominated by capillary condensation in mesopores, and the si2e of the adsorption-desorption hysteresis loop increases, because the pore volume previously occupied by water at the lower pressures now remains empty until the water pressure reaches pressures 0.3 to 0.4 times the vapor pressure) at which capillary condensation can occur. [Pg.277]

By 1980, research and development shifted from relatively inexpensive surfactants such as petroleum sulfonates to more cosdy but more effective surfactants tailored to reservoir and cmde oil properties. Critical surfactant issues are performance in saline injection waters, adsorption on reservoir rock, partitioning into reservoir cmde oil, chemical stabiUty in the reservoir, interactions with the mobiUty control polymer, and production problems caused by resultant emulsions. Reservoir heterogeneity can also greatly reduce process effectiveness. The decline in oil prices in the early 1980s halted much of the work because of the relatively high cost of micellar processes. [Pg.194]

The pH of a 1% solution of pure sodium tripolyphosphate is 9.9 and that of commercial samples may vary between 9.5 and 10.1. The pH of a given sample of solid STP drops slowly with age because of water adsorption and partial reversion to orthophosphate and pyrophosphate. The pH of solutions varies with concentration because the sodium ion is bound in the complex form NaP O o higher concentrations maximum pH is reached at between 1—2% solution. [Pg.337]

If objective is to recover adsorbed components (free of water vapor), inlet gas stream should be dried before molecular sieve adsorption process occurs (water adsorption on mol sieves is particularly strong because of polarity of surface). [Pg.458]

Fig. 9. Water adsorption isotherms at 25°C (to convert kPa to mm Hg, multiply by 7.5). 4A and 5A designate molecular sieves. Fig. 9. Water adsorption isotherms at 25°C (to convert kPa to mm Hg, multiply by 7.5). 4A and 5A designate molecular sieves.
Personnel are protected in working with tritium primarily by containment of all active material. Containment devices such as process lines and storage media are normally placed in well-ventilated secondary enclosures (hoods or process rooms). The ventilating air is monitored and released through tall stacks environmental tritium is limited to safe levels by atmospheric dilution of the stack effluent. Tritium can be efficiently removed from air streams by catalytic oxidation followed by water adsorption on a microporous soHd absorbent (80) (see Absorption). [Pg.16]

A. E. Sherwood, Tritium Removalfrom Air S treams by Catalytic Oxidation and Water Adsorption, Eawrence Eivermore Eaboratoy Report UCRE-78173, 1976. [Pg.17]

Adsorbents Table 16-3 classifies common adsorbents by structure type and water adsorption characteristics. Structured adsorbents take advantage of their crystalline structure (zeolites and sllicalite) and/or their molecular sieving properties. The hydrophobic (nonpolar surface) or hydrophihc (polar surface) character may vary depending on the competing adsorbate. A large number of zeolites have been identified, and these include both synthetic and naturally occurring (e.g., mordenite and chabazite) varieties. [Pg.1500]

For a polar surface and molecules with permanent dipole moments, attraction is strong, as for water adsorption on a hydrophilic adsorbent. Similarly, for a polar surface, a molecule with a permanent quadrupole moment vidll be attracted more strongly than a similar molecule with a weaker moment for example, nitrogen is adsorbed more strongly than oxygen on zeolites (Sherman and Yon, gen. refs.). [Pg.1503]

OH- ions combine with ions of some metals to form insoluble metal hydroxides (precipitation). Precipitated metals settle out and thus are removed from the water adsorption, using activated carbon, improves this separation process. Iron is one of many metals which is commonly removed in this way. [Pg.84]

Ab initio moleeular dynamies has been used to study water adsorption and dissoeiation on MgO [215,216] and on Ti02 [217]. Water is weakly physisorbed on the perfeet MgO (001) surfaee, but dissoeiates readily on the stepped surfaee. Dissoeiative adsorption is observed at fivefold-eoordi-nated Ti sites on the Ti02 (110) surfaee. [Pg.377]

The dried polyoxazoline-modified silica gel was immersed into distilled water. The adsorption property of the resulting gel was estimated by the water content. The water uptake was calculated from an expression of (W -W)jW, where Wis the weight of dried gel and W is the weight of water-absorbed gel. The modified gel showed a higher water-adsorption property than that of untreated silica gel, which absorbed 10.8 multiples of water. The water uptake of modified gel was up to 13.7 multiples of the weight of dried gel. Thus, silica gel has been made more hydrophilic by a polyoxazoline segment. [Pg.24]

The obtained gels were purified by Soxhlet extraction with chloroform to remove the unreacted polyoxazoline. Table 6 summarizes the results of the preparation of polymer hybrids together with their water adsorptions. In comparison with the silica gel without polyoxazoline segments, the modified silica with 50% polyoxazoline was found to show higher water adsorption. [Pg.24]

Table 6. Preparation and water adsorption property of POZO modified silica gel... Table 6. Preparation and water adsorption property of POZO modified silica gel...
A variation of this approach has recently been provided by Lyakhov et al. [598] who, from measurements of water adsorption on CuS04 5 H20, on MgS04 7 H20, and on their respective dehydration products, discern a correlation between strengths of surface bonding and S—T behaviour. At low surface coverages, the mutual dipole—dipole repulsions in the adsorbed layer inhibit water loss, in part by a blocking action on loss of water of crystallization and in part by polarization effects which provide a... [Pg.126]

There are no direct, reliable measurements of 0 based upon adsorption of water from the gas phase. Therefore, 4.25 eV applies to a macroscopic water layer as in the electrochemical configuration. The decrease in 0 upon water adsorption is a general occurrence with metals. The value of A0 observed with Hg is the lowest among those available in the literature.35,36 With reference to Eq. (20), this means that the perturbations of the surfaces of the two phases are small for the Hg/water contact. In other words, the interaction between Hg and water is weak (hydrophobic). [Pg.16]

On the other hand, if the 0 of Hg in the stream is modified by contamination in the cpd measurement, this should not be the case during the measurement of the potential-of-zero charge. If the value of 4.8 eV is accepted for the SHE in the UHV scale, the value of 4.61 eV for < of Hg at the pzc would imply that for 0 to decrease upon water adsorption, the 0 of clean Hg should be substantially higher than 4.61 eV. No experimental evidence exists for this for the time being. [Pg.17]

The discrepancy would be resolved if about 4.8 eV were the actual work function of clean Hg. In this case, however, it would be difficult to understand why 4.50 eV has been consistently measured it is hard to imagine what kind of contamination is responsible for such a highly reproducible situation. On the other hand, if 4.80 eV were the value of for clean Hg, then most of the other metals would show a decrease in work function upon water adsorption less negative than Hg, which is at variance with the expected chemistry of metal surfaces (see later discussion). [Pg.18]

In principle, a measurement of upon water adsorption gives the value of the electrode potential in the UHV scale. In practice, the interfacial structure in the UHV configuration may differ from that at an electrode interface. Thus, instead of deriving the components of the electrode potential from UHV experiments to discuss the electrochemical situation, it is possible to proceed the other way round, i.e., to examine the actual UHV situation starting from electrochemical data. The problem is that only relative quantities are measured in electrochemistry, so that a comparison with UHV data requires that independent data for at least one metal be available. Hg is usually chosen as the reference (model) metal for the reasons described earlier. [Pg.18]

Good agreement between C(- and the dipole moment of the solvent (H20) molecules (i.e., by the hydrophilicity of metals) established by Trasatti25,31 was found and the reasons for this phenomenon were explained 428 The Valette and Hamelin data150 251 387-391 are in agreement with the data from quantum-chemical calculations of water adsorption at metal clusters 436-439 where for fee metals it was found that the electrode-H20 interaction increases as the interfacial density of atoms decreases. [Pg.76]

Water adsorption and dissociation on Ni( 111) and Nig(6 + 2) clusters have been studied by ab initio quantum-chemical calculations.744 "746... [Pg.128]

This equation has been derived only as a reference for a comparative discussion of data for sd- and d-metals later on. However, the meaning of such a line is that there exists a limit to AX values in the sense that after a given top effect, a further increase in metal-water interaction will not produce higher AX values.6,7 An indirect confirmation of this is given by the observation of a top value in the decrease of 0 upon water adsorption on d-metals from the gas phase.35,36... [Pg.163]

Conversion of Earno into an absolute (UHV) scale rests on the values of ff-0 and for Hg used as areference surface. While the accuracy of is indisputable, the experimental value of contact potential difference between Hg and H20, are a subject of continued dispute. Efforts have been made in this chapter to try to highlight the elements of the problem. However, a specialized experimental approach to the measurement of 0 (and A0 upon water adsorption) of Hg would definitely remove any further ambiguity as well as any reasons not to accept certain conclusions. [Pg.190]

Quantum chemical calculations, 172 Quantum chemical method, calculations of the adsorption of water by, 172 Quantum mechanical calculations for the metal-solution interface (Kripsonsov), 174 and water adsorption, 76 Quartz crystal micro-balance, used for electronically conducting polymer formation, 578... [Pg.641]


See other pages where Water ADSORPTION is mentioned: [Pg.663]    [Pg.118]    [Pg.119]    [Pg.120]    [Pg.498]    [Pg.279]    [Pg.449]    [Pg.162]    [Pg.163]    [Pg.35]    [Pg.491]    [Pg.531]    [Pg.410]    [Pg.630]    [Pg.580]    [Pg.371]    [Pg.139]    [Pg.403]    [Pg.20]    [Pg.177]   
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Adsorption Nitrogen, Water vapor

Adsorption and desorption of water

Adsorption at air-water interface

Adsorption at oil-water

Adsorption at oil-water interface

Adsorption from water

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Adsorption isotherm for water

Adsorption isotherms of water vapor

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Adsorption of Water and Organics

Adsorption of organic compounds onto activated carbon applications in water and air treatments

Adsorption of water

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Adsorption-desorption water interface

Air/water interface adsorption

Aqueous-phase solvation water adsorption

Bromine—water adsorption

Carbon Adsorption in Water Treatment

Cellulose Fibers water adsorption

Dichloroethane /water systems adsorption

Dissociative water adsorption

Ethanol water removal from, by adsorption

Fibers water vapor adsorption

Fluorinated zeolites water adsorption

Gold, water adsorption

McBain water adsorption

Mechanical water interface, surfactant adsorption

Multilayer adsorption water

Parameters, water adsorption

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Powders water adsorption

Proteins water adsorption isotherms

Reversible adsorption of water

Rutile, water adsorption

Silica water interface, adsorption

Silicate minerals, adsorption water

Silver water adsorption

Solvent adsorption water effects

Specific surface area water adsorption

The Adsorption of Water on Metal Surfaces

Water Adsorption fibers

Water adsorption 710 INDEX

Water adsorption coefficients

Water adsorption isotherm

Water adsorption mechanisms

Water adsorption microcalorimetry

Water adsorption on Pt and Cu surfaces

Water adsorption, dynamic

Water adsorption, essentially

Water adsorption, essentially hydrophobic surfaces

Water adsorption, selectivity

Water adsorption, supported aqueous-phase

Water carbon adsorption

Water carbon dioxide adsorption effects

Water exchange adsorption rate constants

Water surfaces, adsorption

Water vapor adsorption

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Water vapor adsorption diffusion

Water vapor adsorption equation

Water vapor adsorption generation

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