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Binding of Volatiles

Comparative aroma dilution analyses of the headspace of aqueous solutions, containing either the total volatiles isolated from a fresh coffee brew or these volatiles mixed with the melanoidins isolated from coffee brew, revealed drastic losses of odorous thiols, 2-furfurylthiol, 3-methyl-2-butenethiol, 3-mercapto-3-methylbutyl formate, 2-methyl-3-furanthiol, and methanethiol, in the presence of melanoidins.509 The first compound was affected most, the reduction being 16-fold, and was accompanied by an overall reduction in roasty-sulfury aroma. The rapid loss of thiols was confirmed by stable-isotope dilution analysis. [2H]-NMR and LC-MS gave strong evidence that the thiols become covalently bound via Maillard-derived pyrazinium compounds. [Pg.142]

Hofmann and Schieberle509 also carried out model experiments employing synthetic 1,4-diethyl diquatemary pyrazinium ions with, for example, 2-furfurylthiol, showing that the primary products were 2-(2-furyl)methylthio-l,4-dihydropy-razine, bis[2-(2-furyl)methylthio-l,4-dihydropyrazine], and 2-(2-furyl)methyl-thiohydroxy-l,4-dihydropyrazine. This supports the interpretation of the binding of the thiols as being covalent to pyrazinium intermediates. [Pg.142]

In earlier work with unfractionated coffee melanoidins, Hofmann el al.510 had already shown significant reductions of thiols in the headspace above aqueous model systems on addition of melanoidins, whereas aldehydes remained unaffected. [Pg.142]


Ten aspects of the Maillard reaction will be considered in this chapter the effect on a,, on pH, on redox potential, on solubility, on texture, on foamability and foam stability, on emulsifying power, on volatile formation on storage, on binding of volatiles, and on other functionalities. The third of these has received by far the most attention and this is reflected here. [Pg.124]

The effects upon the secondary structure of poly(L-lysine) upon binding of volatile anesthetics (chloroform, halothane, and enflurane) have been studied through perturbations induced... [Pg.329]

The binding of volatile flavouring substances to dry and air-equilibrated potato starch (which has an 8.2% water content) has also been studied [6,11 [. As one would expect, the moist starch binds more flavour than the dry one. Some of the bound substances are not even released in a vacuum at ambient temperatures and above when water is added, however, the bond is destroyed. [Pg.443]

Finally, let us summarize the type of binding of volatile flavouring substances to various carbohydrates - as far as it is known (Table 5.1). In essence, this is a matter of reversible physical and physico-chemical binding (adsorption, inclusion complexes, hydrogen bridges), so that, in principle, flavour release takes place in the oral cavity. [Pg.444]

O Keefe, S.E A.R Resurreccion L.A. Wilson PA. Murphy. Temperature effect on binding of volatile flavor compounds to soy protein in aqueous model system./. FoodSci. 1991b, 56, 802-806. [Pg.269]

Zhou, Q. K.R. Cadwallader. Effect of flavor compound chemical structure and environmental relative humidity on the binding of volatile flavor compounds to dehydrated soy protein isolates. J. Agric. Food Chem. 2006, 54, 1838-1843. [Pg.274]

Binding of Volatile Aroma Substances to Nutrients and Foodstuffs. Proc. int. Symp. Aroma Research, Zeist, p. 143. Wageningen Pudoc. 1975. [Pg.510]

KL Franzen, JE Kinsella. Parameters affecting the binding of volatile flavor compounds in model food systems. I. Proteins. J Agric Food Chem 22 675-678, 1974. [Pg.174]

Hamanaka, T, Nakagawa, T, Kito, Y., Nishimura, S., Uchida, 1., and Mashimo, T, Binding of volatile anesthetics to purple membranes studied by x-ray diffi action, Toxicol. Lett., 100-101, 397-403,1998. [Pg.2652]

Three methods were used in this research to measure the extent of binding of organic pollutants to dissolved humic materials. They were equilibrium dialysis, solubility measurements and changes in sorption behavior in the presence of humic materials. Other authors have used solubility measurements, ultrafiltration and volatilization measurements. The methods will be described in the following paragraphs. [Pg.217]

The difference between the concentration in the ultra-filtered water and the concentration inside the ultrafiltration cell is therefore a measure of the bound concentration. Griffin and Chian7-7-, Hassett 7-, and Diachenko have used volatilization measurements to determine the extent of binding of pesticides and pollutants to dissolved humic materials. In these experiments either the rate of gas stripping of a compound or its equilibrium vapor pressure is measured in the presence and absence of humic materials. The results obtained can be manipulated in such a way to determine the percentage of the pollutant bound. [Pg.218]

Substances that can potentially be taken up across the skin include gases and vapors, liquids and particulates. Liquids and substances in solution are taken up more readily than dry particulates. Dry particulates will have to dissolve into the surface moisture of the skin before uptake can begin. Absorption of volatile liquids across the skin may be limited by the rate at which the liquid evaporates off the skin surface. As a result of binding to skin components, the uptake of chemicals with the following groups can be slowed certain metal ions, acrylates, quaternary ammonium ions, heterocyclic ammonium ions, and sulfonium salts. [Pg.105]

Hydrogen bond involving an acidic hydrogen atom borne by a fluorine-substituted or halogen-substituted carbon seems to contribute to the activity and the selectivity of volatile fluorinated anaesthetics (Table 2). These molecules, although non-functional, can bind stereoselectively with protein targets of the central nervous system [33,34]. [Pg.561]

Metal reclamation from acid mine drainage and contaminated surface- and groundwater and wastewaters has been extensively studied. Technologies for metal removal from solution are based on the microbial—metal interactions discussed earlier the binding of metal ions to microbial cell surfaces the intracellular uptake of metals the volatilization of metals and the precipitation of metals via complexation with microbially produced ligands. [Pg.328]


See other pages where Binding of Volatiles is mentioned: [Pg.411]    [Pg.142]    [Pg.514]    [Pg.428]    [Pg.439]    [Pg.446]    [Pg.304]    [Pg.311]    [Pg.140]    [Pg.158]    [Pg.411]    [Pg.142]    [Pg.514]    [Pg.428]    [Pg.439]    [Pg.446]    [Pg.304]    [Pg.311]    [Pg.140]    [Pg.158]    [Pg.350]    [Pg.534]    [Pg.58]    [Pg.62]    [Pg.68]    [Pg.598]    [Pg.54]    [Pg.59]    [Pg.134]    [Pg.405]    [Pg.251]    [Pg.64]    [Pg.359]    [Pg.155]    [Pg.279]    [Pg.288]    [Pg.37]    [Pg.162]    [Pg.102]    [Pg.808]    [Pg.973]    [Pg.314]    [Pg.399]    [Pg.609]    [Pg.123]   


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