Environmental Engineering Reference
In-Depth Information
media such as dissolved oxygen or water, resulting in for-
mation of passive layers over the surface of nFe
0
. h is pas-
sive layer hinders the access of target contaminants to nFe
0
,
resulting in the loss of reactivity and degradation ei ciency.
Furthermore, due to size ef ects and high surface energy,
nanoparticles tend to aggregate rapidly, resulting in forma-
tion of much larger clusters which may or may not rel ect the
properties of their nanoconstituents. In addition, aggrega-
tion also decreases the surface area, which in turn impedes
the overall reactivity of the nanoparticle. To address these
issues, several strategies such as use of stabilizing agent, sup-
ports, immobilization/encapsulation, etc., have been devel-
oped, which not only prevent aggregation but also resist
oxidation, prolonging the life of reactive nFe
0
[24, 25, 35, 65].
•
pH:
h e
pH plays a detrimental role in corrosion of iron and
thus indirectly controls the degradation of contaminants.
h e lower pH is responsible for (a) acceleration of corrosion
of iron, and (b) an increase in the aqueous solubility of fer-
rous (Fe
2+
) and ferric (Fe
3+
) ions, yielding less iron hydroxide
precipitates on the surface of nFe
0
and more exposed reac-
tive sites [35]. However, an extremely low pH does not favor
the contaminant reduction reaction. h is can be explained
by intensive corrosion of iron at extremely acidic pH, which
results in an abrupt production of hydrogen which may pro-
duce a blanket of gas bubbles around the surface of nFe
0
,
inhibiting the contact of contaminant species to nanopar-
ticles; hence the overall degradation rate decreases [66]. At
higher pH, Fe
2+
and Fe
3+
from iron surface and OH ions in
the alkaline solution react to precipitate iron oxides/hydrox-
ides on the surface of iron occupying the reactive sites, thus
hindering the access of contaminant species to the reactive
sites, reducing the reaction rate [67, 68].
•
Dosage/Loading:
h e reactivity of nanoparticles is a func-
tion of concentration of reactive sites. With the increase in
nFe
0
dosage, there is a corresponding increase in the num-
ber of reactive sites. h e greater the number of reactive sites,
the greater the number of target molecules accessing the site,
hence the rate of reaction is greater [20, 38, 69]. Alternatively,
if the concentration of the target contaminant exceeds the
number of reactive sites available for reaction, there will be a
decrease in the rate of reaction.
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