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Electrodialytic process offers a range of possibilities to waste management by electrodialytic separation (EDS) of heavy metals, depending on how the process is designed.
The aim of the experiment was to assess quantitatively the elemental interactions' contribution in essential elements and heavy metals, to roots, leaves, sprouts, and whole plant, by studying the interactions between the macro-, micro-elements and heavy metals, depending on their synergism or antagonism.
A previous study by Ko et al. [36] reported the variation of accumulation patterns of trace metals depending on the type of cultivar.
Of particular interest is the electronic property of SWNTs, which are seamlessly rolled-up graphene sheets of carbon, behaving either as semiconductors or as metals depending on its diameters and chiralities [11].
Some biosorbents are non-selective and bind to a wide range of heavy metals with no specific priority, whereas others are specific for certain types of metals depending on their chemical composition.
These pollution-causing heavy metals come from various industrial sources such as mining, photographic industries, battery manufacture, paints manufacture, electroplating, cosmetics, etc. Natural waters also contain toxic metals depending on bedrocks (Obuseng et al. 2012).
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Theoretical and experimental observations have shown that the fracture behaviour of many metals depends on the stress state.
Thermopower of metals depends on a number of factors.
The co-ordination bond formation phenomena of metals depend on the co-ordination number.
This is well known since the magnetic moment of transition metals depends on volume [8].
It is known that accumulation of metals depends on physicochemical properties of metals and physiology of organisms.
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