S Ayoob; A K Gupta; Venugopal Bhat's A Conceptual Overview on Sustainable Technologies for the PDF

By S Ayoob; A K Gupta; Venugopal Bhat

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Extra info for A Conceptual Overview on Sustainable Technologies for the Defluoridation of Drinking Water

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Determining the volume of mercury that can be forced into the pores, as a function of pressure), it is possible to determine the relative numbers of pores of a given size. This information is usually expressed as a plot of "cumulative pore volume" versus pore diameter. The cumulative pore volume corresponding to any pore diameter value represents the total volume contained in pores of that diameter or less. 2 shows a typical distribution. The steepest part of the curve represents the pore diameter range with which most of the pore volume is associated.

Yet such is not always true. One must be aware that the surface area is usually inferred from the amount of N 2 (a small molecule) which can be adsorbed at -196°C (N2 boiling point). If one wishes to adsorb a large molecule, much of the internal surface area may not be accessible. 5 gives an example of this. 10 g/liter. From Hassler (1963). Reprinted by permission of the Chemical Publishing Company. were initially too small to admit the large molecules of aniline blue finally become large enough to admit them.

And Schochet, S. S. (1931). Studies in adsorption. I. The adsorption of physiologically active substances by activated charcoal, J. Pharmacol. 42, 169. Sears, Roebuck, and Company (1969). 1908 Catalog No. 117 (reprint), Digest Books, Northfield, Illinois, p. 790. Sjogren, B. and Wallden, E. (1935). The adsorbing power of medicinal charcoal, Svensk. Farm. Tid. 39, 617, 632, 673, 697, 720. Suchy, J. F. and Rice, R. V. (1935). Adsorption of strychnine sulfate by various charcoals and by Lloyd's reagent, J.

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A Conceptual Overview on Sustainable Technologies for the Defluoridation of Drinking Water by S Ayoob; A K Gupta; Venugopal Bhat

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