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Site quantitation

SSZ-35 the reactions would be influenced by the presence of very strong Lewis sites. Quantitative sorption of ammonia, pyridine and d3-acetonitrile in both zeolites showed that the real number of acidic groups was close to values, derived form the number of aluminum atoms (taken from AAS analysis) in the idealized unit cell. Obtained values are 1.1 H+/u.c. for SSZ-33 with idealized unit cell composition H2.9[Al2.9Si53.iOii2] (plus 1.3 Lewis sites per u.c.) and 0.3 H+/u.c. for SSZ-35 with ideal formula Ho.4[Alo.4Sii5 6032] (plus 0.05 Lewis sites per u.c.). [Pg.275]

Exposure Levels in Environmental Media. Tetryl has been detected in seepage water, groundwater, and surface and subsurface soil at military installations (Army 1980, 1981b, 1986a, 1988, 1990b ATSDR 1987 HazDat 1994). More data are needed regarding levels of tetryl in surface water, groundwater, soil, and air in and around these sites. Quantitative information is needed to assess the potential for human exposure and to better identify exposed populations. [Pg.62]

Discovery of Galactic Li-rich red giants (McKellar 1940) came years before either the proposal of the 7Be-transport mechanism or the identification of a luminous AGB star with a HBCE as a plausible site. Quantitative checks on production in such AGB stars (Sackmann Boothroyd 1992) were made possible with the discovery of Li-rich AGB stars in the LMC and SMC (Smith Lambert 1989, 1990 Plez et al. 1993) - see Fig. 3. These are being extended through observations of AGB stars in Magellanic Cloud clusters. Reliable distances to the Clouds enable the stellar luminosity and mass to be estimated, a task impossible with any precision for Galactic field stars. Confrontation of theory and observation confirmed that Li-production occurs in AGB stars of about 4-6 M0 at about the predicted level. Several factors stand between this result and an assessment of AGB stars as 7Li factories effective on the galactic scale. Uncertainties surround both the production of 7Li via the 7Be-transport mechanism and the return of the 7Li via the stellar winds. [Pg.97]

Trace metals are held in deposited sediments in a number of different sites . First of all there are metals in the mineral lattices (often referred to as the residual phase metals). In uncontaminated sediments, this is normally the most important site quantitatively. Secondly, trace metals, particularly anthropogenically introduced metals, occur associated with particle surfaces, hence there is often a significant correlation between trace metal content and grain-size or surface area, which is in turn related to the sediment mineralogy (Figure 2.1). There has been a lot of detailed work in recent years on the mode of occurrence of trace metals in sediments and one of three different approaches is normally taken. [Pg.17]

As shown by Cheetham and coworkers [51,52], these paramagnetic chemica] shift effects can be exploited for site quantitation purposes. Figure 9 provides a nice illustration for a sample with the nominal composition YSmSn207. Figure 9a shows the nearest and next-nearest neighbor coordination environment of the Sn atoms in the pyrochlore structure. The Sn atoms are at the center of an Sn06... [Pg.211]

At least for the present, proton saturation transfer experiments will be the most tractable. For accurate measurement of the degree of saturation, adequate time must have elapsed for equilibrium to be established. This time is on the order of five times the relaxation time, or k. Hence, for the gated decoupling of the protons in (7) -allyl)Fe(CO)3l, decoupling must be carried out for 10-20 seconds before the 90° pulse to achieve reproducible results. A second feature, which can often be observed in syn and anti protons, is the signal enhancement arising from the nuclear Overhauser effect (NOE). Thus, the observed intensity is a function of both the NOE and the magnetization transferred into the site. Quantitative determinations must correct for the NOE enhancements. [Pg.222]

TABLE 1. Herbicide ( C-diuron) binding affinity and binding site quantitation on a chlorophyll basis in wildtype Svnechocvstis and the hybrid mutants. [Pg.360]

The observed rate of adsorption of CO does not quite have the expected Langmuir form where the rate of adsorption is proportional to the fraction of empty sites. This is because CO is initially trapped in a mobile precursor site. Quantitative agreement with the experimental oscillations requires using (Sco/ cosat) with a power higher than unity, say between 3 and 4. [Pg.493]

More quantitative results are available for the nitration of alkyl-thiazoles Dou et al. (373) determined the reactivity, relative to benzene, of the nitration site of various mono- and dialkylthiazole by competition experiments (Table 1-53). [Pg.104]

The iodine number of fats and oils provides a quantitative measurement of the degree of unsaturation. A solution containing a 100% excess of IGl is added to the sample, reacting across the double-bonded sites of unsaturation. The excess IGl is converted to I2 by adding KI. The resulting I2 is reacted with a known excess of Na2S203. To complete the analysis the excess 8203 is back titrated with coulometrically generated I2. [Pg.534]

Equation 6 shows that the adsorption of component 1 at a partial pressureis reduced in the presence of component 2 as a result of competition for the available surface sites. There ate only a few systems for which this expression (with 5 1 = q 2 = 5 ) provides an accurate quantitative representation, but it provides useful quaUtative or semiquantitative guidance for many systems. In particular, it has the correct asymptotic behavior and provides expHcit recognition of the effect of competitive adsorption. For example, if component 2 is either strongly adsorbed or present at much higher concentration than component 1, the isotherm for component 1 is reduced to a simple linear form in which the apparent Henry s law constant depends onp. ... [Pg.256]

The stmctural architecture of siUcone polymers, such as the number of D, T, and Q sites and the number and type of cross-link sites, can be deterrnined by a degradative analysis technique in which the polymer is allowed to react with a large excess of a capping agent, such as hexamethyidisiloxane, in the presence of a suitable equiUbration catalyst (eq. 38). Triflic acid is often used as a catalyst because it promotes the depolymerization process at ambient temperature (444). A related process employs the KOH- or KOC2H -catalyzed reaction of siUcones with excess Si(OC2H )4 (eq. 39) to produce ethoxylated methylsiUcon species, which are quantitatively deterrnined by gc (445). [Pg.59]


See other pages where Site quantitation is mentioned: [Pg.249]    [Pg.136]    [Pg.89]    [Pg.165]    [Pg.14]    [Pg.93]    [Pg.152]    [Pg.108]    [Pg.354]    [Pg.195]    [Pg.89]    [Pg.249]    [Pg.136]    [Pg.89]    [Pg.165]    [Pg.14]    [Pg.93]    [Pg.152]    [Pg.108]    [Pg.354]    [Pg.195]    [Pg.89]    [Pg.701]    [Pg.1490]    [Pg.1493]    [Pg.1515]    [Pg.2108]    [Pg.2977]    [Pg.136]    [Pg.327]    [Pg.108]    [Pg.248]    [Pg.91]    [Pg.389]    [Pg.59]    [Pg.221]    [Pg.489]    [Pg.29]    [Pg.147]    [Pg.272]    [Pg.275]    [Pg.475]    [Pg.474]    [Pg.87]    [Pg.215]    [Pg.6]    [Pg.235]    [Pg.244]   
See also in sourсe #XX -- [ Pg.125 ]




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Quantitation of Sites

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