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Additive desorption

Another major computational effort is in the area of metals and their chemistry, which comprises the subject of this manuscript. The studies are directed towards both catalysis and the development of improved materials, such as stronger matrix composites. The materials and gas phase work have some overlap. For example, surface recombination affects the heating on the AOTV heat shield and on the walls of the scramjet. In addition, desorption of these molecules from the walls of the scramjet could impact the chemistry in the flow. [Pg.17]

Figure 2.9 Thermal desorption of carbon monoxide from two rhodium surfaces in ultrahigh vacuum, as measured with the experimental set-up of Fig. 2,10. Each curve corresponds to a different surface coverage of CO. At low coverages CO desorbs in a single peak indicating that all CO molecules bind in a similar configuration to the surface. At higher coverages, an additional desorption peak appears, indicative of a different adsorption geometry (courtesy of M.J.P. Hopstaken and W.E. van Gennip [141). Figure 2.9 Thermal desorption of carbon monoxide from two rhodium surfaces in ultrahigh vacuum, as measured with the experimental set-up of Fig. 2,10. Each curve corresponds to a different surface coverage of CO. At low coverages CO desorbs in a single peak indicating that all CO molecules bind in a similar configuration to the surface. At higher coverages, an additional desorption peak appears, indicative of a different adsorption geometry (courtesy of M.J.P. Hopstaken and W.E. van Gennip [141).
Most soil-pesticide sorption-desorption studies have used batch techniques, which create several problems. In many batch studies the slow portion of the soil-pesticide interactions may not be seen if observation times are too short (McCall and Agin, 1985). Additionally, desorption is usually begun by centrifuging the equilibrated soil-pesticide system, removing a known volume of pesticide solution, replacing with the same volume of pesticide-free solution, and resuspending the soil-pesticide solution. This procedure is then repeated to develop desorption isotherms initiated from a particular point on the sorption isotherm. Then there is... [Pg.137]

An empirical non-linear model was used to describe the bi-phasic nature of desorption with one fraction (labile) being released in relatively short periods of time (typically 24-100 h) and a second fraction (non-labile or irreversible) being resistant to desorption and the parameters estimated. In addition, desorption kinetics of three-month and five-month old contaminated soils showed that progressively less amount of contaminant was available for labile desorption (lower F) compared to freshly contaminated soil. [Pg.134]

Figure 3 Sorption and desorption edges for uranyl on goethite. Each sample contained 60m L goethite and 100p,gmL uranium. The sorption edge was measured 2 d after uranium addition desorption samples were contacted with the uranyl solution at pH 7 for 5 d, the pH was adjusted to cover the range of interest, and the samples were re-equilihrated for 2 d prior to sampling (see also Bryan and Siegel, 1998). Figure 3 Sorption and desorption edges for uranyl on goethite. Each sample contained 60m L goethite and 100p,gmL uranium. The sorption edge was measured 2 d after uranium addition desorption samples were contacted with the uranyl solution at pH 7 for 5 d, the pH was adjusted to cover the range of interest, and the samples were re-equilihrated for 2 d prior to sampling (see also Bryan and Siegel, 1998).
The amount of adsorbed CO on Pt/Ce/Al203 is about six times of that adsorbed on Pt/Al203. The TPD spectrum of Pt/Ce/Al203 shows an additional desorption peak at about 200°C, as shown in Figure 1. The addition of ceria seems to stabilise the noble metal dispersion. The cobalt containing catalysts all give similar TPD spectra, as shown in Figure 1,... [Pg.115]

Abstract The controlled in-situ deposition of sexiphenyl (6P) on the (2x1) oxygen reconstruction of Cu (110) is shown to give rise to the ordered growth of large anisotropic needle-like structures on the surface. Photoemission electron microscopy (PEEM) and atomic force microscopy (AFM) results are presented for the growth of 6P (20-3) crystalline needles for a range of substrate temperatures. In addition, desorption and other interesting phenomena are discussed. [Pg.149]

Adsorbent trap. This method needs an additional desorption step with a small volume of eluent. For selecting suitable eluent one should consider ... [Pg.63]

On the other hand, well-defined adsorption isotherms of proteins have been reported. Figure 1 shows one example, that for chymotrypsin in pure water at 20 C. The attainment of steady surface pressure values, which Increase with increasing protein concentration in solution indicating true equalization of bulk and surface chemical potentials, argues in favor of a reversible adsorption process. In addition, desorption from protein monolayers has been measured. How to rationalize these apparently conflicting results therefore presents an intriguing challenge. [Pg.166]

There are some principal disadvantages that limit the use of fiber SPME. These include fhe limited capacity of SPME fiber and a requiremenf for a very low initial temperature for GC temperature programs because of the necessity of cryofocusing of the analyte, thus prolonging GC analysis time. In addition, desorption takes more time than in the injection of LEE or SPE extracts, and carryover effects occur very easily. As SPME is by nature a dirty extraction, quantification is more prone to errors due to changes in the matrix even when internal standards are used. Finally, SPME fiber is quite fragile. Because of these restrictions and limitations, fiber SPME is not a universal sample preparation method, especially not in bio-analytical laboratories, and is unlikely to become so in the future. [Pg.136]

In addition, desorption of the surface adsorbed species produces NO2 independent of whether NO (with O2) or NO2 was the reactant. Hence, and in agreement with other experimentation (4-7), NO2 is considered to be the adsorbed species and the desorbed product for our conditions of testing. When O2 was a co-reactant, the adsorption capacity of carbon for either NO or NO2 was found to be identical. However, without O2 the adsorption capacity for NO2 was slightly less than for NO2 with coreactant O2, thereby suggesting O2 also aided the adsorption of NO2. The temperature of maximum desorption was IQPC higher when NO2 was used as the adsorbate as compared to NO with coreactant O2. This difference in desorption temperatures indicates that surface oxygen, adsorbent-adsorbate interactions, or other factors are yet to be defined which determine NO and NO2 adsorption mechanisms on carbon. [Pg.209]

Displacement Desorption Here, an additional desorption medium, which is preferably adsorbed by the adsorbent displaces the adsorbed component. The desorption medium has to be chosen in such a way, that it is easily separated from the adsorbate. Figure 4-21 shows an adsorption plant for the separation of a mixture of normal and iso-... [Pg.314]

Desorption efficiency is affected by temperature, trap heating rate, and desorb-gas flow rate. Analytes are released faster at a higher temperature, which is limited by the thermal stability of the sorbent materials. Also, the faster the trap is heated, the shorter the desorption time. In addition, desorption is more efficient at higher flow rate. The actual flow rate depends upon the GC column used. [Pg.2053]

Due to the open planar surface of UTLC layers, especially ambient desorption- or elution-based techniques were used to transfer analytes from the layer to the ionization region (Table 9.2). In addition, MALDI applications under vacuum were reported and the introduction of the whole ultrathin layer plate was possible without any special mounting devices, due to the small plate dimension. As UTLC-MS is a very new hyphenation, only a few applications of MS detection were reported after separation of different substances on UTLC layers. In addition, desorption- or elution-based approaches for detecting analytes without a separation directly from the UTLC layer are mentioned to show the capabilities of this hyphenation technique. However, as there is no chromatography (separation), it may not be termed UTLC-MS. [Pg.147]

In addition to MALDI, there are additional desorption MS techniques, whereby desorption electrospray (DESI) MS seems particularly versatile [15]. Readers who are particularly interested in DESI MS are referred to the work of Zoltan Takats and his group or another paper dedicated exclusively to TLC/DESI MS of lipids [16]. [Pg.216]

More fundamentally, the relatively low mass-resolution results observed on linear instruments suggest that desorption techniques do not entirely eliminate the problems associated with initial time and space distributions. Detector response times and digitizer sampling rates will in fact limit mass resolution in the short time intervals that are measured on high-voltage instruments, and contribute (essentially) to uncertainties in Atg. In addition, desorption of neutral species (as well as ions) from a 3-to 10-ns laser might well result in ionization above the surface, resulting in unanticipated spatial-distribution problems. [Pg.40]

Sorption and desorption edges for uranyl on goethite. Each sample contained 60 L goethite and uranium. The sorption edge was measured 2 d after uranium addition desorption samples were... [Pg.218]

If, at the end of adsorption, the adsorbate concentration on adsorbent particles is represented by point A (Figure 7.1.8(a)) and tbe temperature is, say, TAdsorptiDii, for desorption tbe temperature is increased to TuesorptiDiw which is higher. The adsorption isotherm now is considerably lower is reduced to a lower value, even if p remains the same. The temperature of the bed is raised by supplying either a hot gas or steam. The hot gas may be obtained using the feed gas itself or some other gas, e.g. air. When the partial pressure of species i in the hot gas is lower than that at point A, there is additional desorption since (PiguTe 7.1.8(c)). After desorption, the... [Pg.505]

Desorption of an adsorbed polymer by flushing with solvent proceeds particularly slowly and, in practice, it is impossible to desorb a significant amount in this way. However, we have seen that desorption of a polymer can be accomplished under the influence of an external shear force. In addition, desorption may be caused by competition with a polymeric or a monomeric displacer. In this section we will discuss exchange by a chemically identical polymer or by a polymer differing in size or chemical composition. [Pg.184]

In addition, desorption and decomposition of propylamines on Ga-ZSM-5 were investigated [260, 261, 266]. The features of these processes were completely different from those observed upon interaction of propylamines with H-ZSM-5. Also, Ga-ZSM-5 prepared via interaction of Ga203 and H-ZSM-5 or H-MOR in a physical mixture was employed as a catalyst for NO reduction by... [Pg.170]


See other pages where Additive desorption is mentioned: [Pg.157]    [Pg.40]    [Pg.152]    [Pg.153]    [Pg.176]    [Pg.72]    [Pg.26]    [Pg.152]    [Pg.153]    [Pg.41]    [Pg.185]    [Pg.81]    [Pg.121]    [Pg.242]    [Pg.422]    [Pg.59]    [Pg.253]    [Pg.16]    [Pg.403]    [Pg.344]   
See also in sourсe #XX -- [ Pg.226 ]




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