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Light and heavy quasiparticles in the metamagnet CeRuâ†2Siâ†2Howard, Bruce Kenneth January 1989 (has links)
No description available.
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F electrons in CePbâ†3McDonough, Johnathan January 1994 (has links)
No description available.
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Physico-chemical studies of metals in the highway environmentWilson, S. J. January 1984 (has links)
No description available.
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Genetic location and transferability of chromium resistance gene(s) among aquatic bacteriaCullen, Daniel W. January 1997 (has links)
No description available.
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ADSORPTION OF HEAVY METALS ON SOIL CLAYS (KAOLINITE, CADMIUM, MONTMORILLONITE, ZINC).PULS, ROBERT WILLIAM. January 1986 (has links)
Metal cation adsorption is the predominant chemical mechanism governing the attenuation of toxic metal movement in soils. Clay minerals are the primary adsorbent surfaces in soils due to their ubiquitous nature and large reactive surface area. This study examined the relative affinity of the metals cadmium, nickel and zinc for the clay minerals kaolinite and montmorillonite. The influence which different mineral adsorbents and different complexing ligands in solution have on the adsorption of metal ions was assessed using the Hard-Soft Acid-Base Principle as a theoretical framework for predicting the maximum extent of adsorption and rate of adsorption. The HSAB principle is that hard bases prefer to complex hard acids and soft bases prefer to complex soft acids. The hypothesis that initiated these investigations was that the hard-soft character of mineral surfaces is due to their surface functional groups and can be measured using metal cation adsorption selectivity experiments where pH and complex ion formation are controlled. When complex ion formation in aqueous solution was minimized (i.e. in Ca(ClO₄)₂), adsorption decreased in the order of decreasing softness, CD > Zn > Ni for both clay minerals. Montmorillonite behaved as a slightly harder Lewis base than kaolinite, sorbing the harder Ni and Zn ions to a greater extent than Cd, although both minerals behaved as soft Lewis bases. In the presence of chloride and sulfate ligands, adsorption sequences changed and reflected results from typical soil solution studies. In some cases the adsorption sequences can be explained using the HSAB principle together with computer speciation data and this approach merits further consideration and research. Adsorption over time and calculated adsorption rate constants were generally consistent with equilibrium selectivity data. Adsorption rates decreased in the order Cd > Zn > Ni in Ca(ClO₄)₂ for both clay minerals. The adsorption curves reflect a two-step adsorption process involving a rapid exchange-type reaction followed by a much slower adsorption involving diffusion into the crystal or alteration of the surface through the formation of a new solid phase involving the adsorbed ions.
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Scattering of polarized lithium-7 form nuclei at energies near the Coulomb barrierKhudeir, Imad January 1991 (has links)
No description available.
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Vanadium toxicity in the yeast, Saccharomyces cerevisiaeHenderson, G. E. January 1988 (has links)
No description available.
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The use of microwave flow-through digestion in the analysis of trace metals and total nitrogen in soilsMason, Christopher James January 2000 (has links)
No description available.
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Bacterial degradation of polycyclic aromatic hydrocarbonsGleisner, Florian Hans January 2001 (has links)
No description available.
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Effects of cadmium toxicity on population dynamics of the blowfly Lucilia sericataDaniels, Susan G. January 1994 (has links)
No description available.
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