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Metal fraction can be treated by pyrometallurgical, hydrometallurgical or biotechnological process [11].
Afterwards, geoaccumulation indexes were calculated in order to estimate the metal fraction of anthropogenic origin.
Physical processing for the separating the metal fraction and non-metal fraction from waste PCBs includes shape separation, magnetic separation, electric conductivity-based separation, density-based separation and corona electrostatic separation.
This effect is obviously explained by the contribution of the metal fraction to the effective dielectric function.
The metal fraction was severely sintered during the APR reaction, irrespective of the reactant size.
The rate correlated with the metal fraction nearly identically for either Pd or Co rich mixtures.
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Open image in new window Fig. 5 Distribution of heavy metal fractions in different amended soils.
Metal fractioning was carried out essentially as described by Rauser and Meuwly (1995).
The estimation of bioavailable metal fractions is, generally, based on single or sequential extraction procedures [5, 6], but these provide only a classification of metal fractions in the soil compartments.
Followed by each treatment, metal fractions varied as a result of chemical reactions between soil particles and amendments.
In this paper, bioavailability considerations are linked to physico-chemical methods available for assessing metal fractions in soils.
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