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Trace elements interactions

Nitrogen and Phosphate Fertilizers and Trace Element Interactions... [Pg.250]

Baalousha, M., Kammer, F. V. D., Motelica-Heino, M., Baborowski, M., Hofmeister, C., and Le Coustumer, P. (2006). Size-based speciation of natural colloidal particles by flow field flow fractionation, inductively coupled plasma-mass spectroscopy, and transmission electron microscopy/x-ray energy dispersive spectroscopy Colloids-trace element interaction. Environ. Sci. Technol. 40(7), 2156-2162. [Pg.528]

Chowdhury BA, Chandra RK. 1987. Biological and health implications of toxic heavy metal and essential trace element interactions. Prog Pood Nutr Sci 11 55-l 13. [Pg.444]

Suttle, N. F. (1975). Trace element interactions in animals. In Trace Elements in Soil-Plant-Animal Systems, ed. D. J. D. Nicholas and A. R. Egan, pp. 271-89. New York Academic Press. [Pg.227]

If the trace element interacts with the major components of the host mineral, the activity will depart from the ideal mixing relationship and at low concentrations the activity composition relations obey Henry s Law. This states that at equilibrium the activity of a trace element is directly proportional to its composition ... [Pg.104]

Chemiluminescence has been studied extensively (2) for several reasons (/) chemiexcitation relates to fundamental molecular interactions and transformations and its study provides access to basic elements of reaction mechanisms and molecular properties (2) efficient chemiluminescence can provide an emergency or portable light source (J) chemiluminescence provides means to detect and measure trace elements and pollutants for environmental control, or clinically important substances (eg, metaboHtes, specific proteins, cancer markers, hormones, DNA) and (4) classification of the hioluminescent relationship between different organisms defines their biological relationship and pattern of evolution. [Pg.262]

Pha.rma.ceutica.1 Purity. A safety profile of a generic dmg can differ from that of the brand-name product because different impurities may be present in each of the dmgs (154). Impurities can arise out of the manufacturing processes and may be responsible for adverse interactions that can occur. Eor example, serious adverse reactions (LyeU syndrome) were observed upon the use of isoxicam in 1985. These seemed to have resulted from trace elements of a manufacturing by-product that was within the manufacturing quaUty control specifications. [Pg.250]

Trace elements added to copper exert a significant influence on electrical conductivity. Effects on conductivity vary because of inherent differences ia effective atomic size and valency. The decrease ia conductivity produced by those elements appearing commonly ia copper, at a fixed atomic concentration, rank as follows Zn (least detrimental), Ag, Mg, Al, Ni, Si, Sn, P, Fe (most). Table 12 summarizes these effects. In the absence of chemical or physical interactions, the increase in electrical resistivity is linear with amounts of each element, and the effect of multiatom additions is additive. [Pg.229]

Electron Probe Microanalysis, EPMA, as performed in an electron microprobe combines EDS and WDX to give quantitative compositional analysis in the reflection mode from solid surfaces together with the morphological imaging of SEM. The spatial resolution is restricted by the interaction volume below the surface, varying from about 0.2 pm to 5 pm. Flat samples are needed for the best quantitative accuracy. Compositional mapping over a 100 x 100 micron area can be done in 15 minutes for major components Z> 11), several hours for minor components, and about 10 hours for trace elements. [Pg.119]

When iodine dissolves in organic solvents, it produces solutions having a variety of colors. These colors arise from the different interactions between the I2 molecules and the solvent (Fig. 15.21). The element is only slightly soluble in water, unless I ions are present, in which case the soluble, brown triiodide ion, I,, is formed. Iodine itself has few direct uses but dissolved in alcohol, it is familiar as a mild oxidizing antiseptic. Because it is an essential trace element for living systems but scarce in inland areas, iodides are added to table salt (sold as iodized salt ) in order to prevent an iodine deficiency. [Pg.761]

In contrast with phosphorus, most metals can exist in a variety of oxidation states and physical forms, which makes them participants in all of the geospheres. However, because metals are generally trace elements for biota, most of the metal cycles are not significantly altered by biological interaction, but rather may affect the... [Pg.280]

Andreae, M. O. (1979). Arsenic speciation in seawater and interstitial waters the role of biological-chemical interactions on the chemistry of a trace element. Limnol. Oceanog. 24,440-452. [Pg.416]

Although Fe is required as a trace element, its uptake is critically regulated since excess leads to the generation of toxic hydroxyl radicals, and complex interactions involving Fe(II) and Fe(HI) exist within the cell (Touati et al. 1995). The role of Fe(III)-complexing siderophores in maintaining homeostasis has been noted in Chapter 3, Part 5. Details of the role of Fe and its relation to the... [Pg.254]

Removal to sediments. Removal of surface-reactive trace elements from the oceans readily occurs by adsorption onto settling particles, and this process is most pronounced in the typically high-energy, particle-rich estuarine environment. Particles are supplied by rivers, augmented by additions of organic material generated within the estuary. Also, floes are created in estuaries from such components as humic acids and Fe. The interaction between dissolved and colloidal species is enhanced by the continuous resuspension of sediments in... [Pg.580]

Table 8.76 shows the main characteristics of voltammetry. Trace-element analysis by electrochemical methods is attractive due to the low limits of detection that can be achieved at relatively low cost. The advantage of using standard addition as a means of calibration and quantification is that matrix effects in the sample are taken into consideration. Analytical responses in voltammetry sometimes lack the predictability of techniques such as optical spectrometry, mostly because interactions at electrode/solution interfaces can be extremely complex. The role of the electrolyte and additional solutions in voltammetry are crucial. Many determinations are pH dependent, and the electrolyte can increase both the conductivity and selectivity of the solution. Voltammetry offers some advantages over atomic absorption. It allows the determination of an element under different oxidation states (e.g. Fe2+/Fe3+). [Pg.670]

Brewer GJ, Hill GM, Dick RD, et al. 1985. Interactions of trace elements Clinical significance. J Am Coll Nutr 4 33-38. [Pg.497]

Carbonates, organic matter, Fe and Mn oxides, and clay minerals play important roles in controlling overall reactivity of trace elements in soils and sediments. This chapter addresses the interaction of trace elements with carbonates, organic matter, Fe and Mn oxides and clay minerals. Analytical techniques for trace element speciation in solid-phase and their distribution among various solid-phase components in arid and semi-arid soils are reviewed. Solubilities of trace elements in solid phases and their mineralogical characteristics in arid and semi-arid soils also are discussed. [Pg.131]

Crop cultivar variation in trace element uptake had been observed with com, rice, barley, wheat, and cocoa (Adriano, 1986). Wheat and soybeans showed variety-based variation of P-Zn interaction. Crop varieties with a low capacity for uptake of Zn in soils were more vulnerable to Zn deficiency by P application. Crops sensitive to Zn deficiency included beans, potatoes, peaches, flax, com, rice, soybeans, and citrus (Adriano, 2001). [Pg.252]

Bradford G.R., Page A.L., Lund L.J., Olmstead W. Trace element concentrations of sewage treatment plant effluents and sludges Their interactions with soils and uptake by plants. J Environ Qual 1975 4 123-127. [Pg.332]

Lombi E., Wenzel W.W., Gobran G.R., Adriano D.C. Rhizosphere-contaminant interaction and its role in phytoremediation A review. Proceedings of the 5th International Conference on Biogeochemistry of Trace Elements, Austria, 1999. [Pg.342]

Of the major solids formed from melts, many, but not all, at equilibrium, the overwhelming influence is of cooperative interaction between ionic units of similar shape and size as we see in crystals. Trace elements apart from forming isolated minerals are fractioned in bulk oxides, for example, in particular orders as the melt solidifies, and this reduces the relative availability of some elements such as Cr and Ni (see Williams, and Williams and Frausto da Silva (1999) in Further Reading). Again the interaction of selective molten minerals and water creates extremely reactive environments and such environments still exist, especially in the deep sea black smokers (hydrothermal vents), around which particular mixed minerals form, which could also have been involved in prebiotic chemistry and are still involved in the peculiarities of life in these smokers . In Figure 1.6 we summarise... [Pg.13]

Numerous and disparate copper criteria are proposed for protecting the health of agricultural crops, aquatic life, terrestrial invertebrates, poultry, laboratory white rats, and humans (Table 3.8) however, no copper criteria are now available for protection of avian and mammalian wildlife, and this needs to be rectified. Several of the proposed criteria do not adequately protect sensitive species of plants and animals and need to be reexamined. Other research areas that merit additional effort include biomarkers of early copper stress copper interactions with interrelated trace elements in cases of deficiency and excess copper status effects on disease resistance, cancer, mutagenicity, and birth defects mechanisms of copper tolerance or acclimatization and chemical speciation of copper, including measurement of flux rates of ionic copper from metallic copper. [Pg.215]

Kirchgessner, M., F.J. Schwarz, E. Grassmann, and H. Steinhart. 1979. Interactions of copper with other trace elements. Pages 433-472 in J.O. Nriagu (ed.). Copper in the Environment. Part 2 Health Effects. John Wiley, NY. [Pg.224]


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See also in sourсe #XX -- [ Pg.1119 ]




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Trace interactions

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