Agriculture Reference
In-Depth Information
wards water and the hydrated radii of the particles were much higher than
their un-hydrated counterparts. Therefore it is very important to get stable
suspension of nano-particles of desired size for harnessing the benefit of
nano-particles.
The zeta potential of the nano-particles is another important param-
eter that has been extensively investigated for stability of nano-particles.
High zeta potential (negative or positive) will impart stability to the nano-
particles suspension, whereas nano-particles with low zeta potentials tend
to coagulate or flocculate ( Table 9.4 ) pH is a major factor determining
the zeta potential of nano-particles. When pH is at point of zero charge
( pzc ) or isoelectric point, the nano-particles exhibit minimum stability
(i.e., exhibit maximum coagulation/flocculation). When the pH is lower
than the pzc value, the nano-particle surface is positively charged and the
zata potential will increase with decreasing pH below the pzc . Conversely,
at pH above pzc , the surface is negatively charged and the zeta potential
will be more negative with increasing pH. The values of pzc of selected
nano-particles are presented in Table 9.5 . The ionic strength of the sur-
rounding aqueous medium is also an important factor affecting the sta-
bility of the nano-particles. When ionic strength is increased and/or the
zeta potential is reduced (both effects usually result from an increased salt
concentration), attractive force between colloids will outweigh the repul-
sion, and the particles can then adhere each time they collide. The surface
charge is also another important property that can dominance the migra-
tion of ENMs in porous media (Darlington et al., 2009). The soil particles
are generally negatively charged. Thus, positively charge ENMs will be
readily electro-statically attracted to the soil surface. Nano-particles with
higher negative charges are believed more mobile in soil matrix because of
the longer electrostatic repulsion between the nano-particles and soil par-
ticles and between nano-particles themselves as well. Therefore, various
methods have been applied to modify ENM surface properties to control
(enhance or restrict) the transport of ENMs in porous media/soil among
which surface functionalization with hydrophilic functional groups (e.g.,
-OH and -COOH) and surface physical modification using polymers or
surfactants are two commonly adopted methods.
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