Environmental Engineering Reference
In-Depth Information
Activated carbon
prepared from
Phaseolus aureus
hulls
325
15.7
1h
8
72.3
30
[103]
Activated carbon
prepared from
olive stone
790.25
1.85
90min
>6
-
20
[113]
Unmodified
activated carbon
725
207.3
120
8
-
30
[106]
Triton X-100-
modified carbon
792.5
232.9
120
8
-
30
[106]
SDS-modified
carbon
805.3
263.2
120
8
-
30
[106]
CTAB-modified
carbon
814.2
279.5
120
8
-
30
[106]
Activated carbon
derived from
bagasse
960
38.03
12h
4.5
-
25
[114]
The biosorption abilities of
Rhodococus opacus
, a unicellular gram
positive bacterium with amphoteric properties, were studied by Vásquez
et al.
[117]. The amphoteric behavior of the cell surface of the
R. opacus
is caused
by the polysaccharides, carboxylic, lipid and micolic acid groups presented on
the surface cell wall. The Cd
2+
adsorption process followed a pseudo second
order kinetic model, suggesting a chemisorption behavior. The maximum
adsorption capacity was 1.56 mg g
-1
.
The Cd
2+
removal from aqueous solution by
Sphingomonas paucimobilis
,
a gram negative bacterium, was studied by Tangaromsuk
et al.
[118]. The
highest percentage of the cadmium removal by live cells
of the
Sphingomonas
paucimobilis
was about 84 % at pH 6, while the highest percentage from pH 5
solutions using dead cells of the
Sphingomonas paucimobilis
was only 28 %.
Zhou
et al.
[119] used exopolysaccharide, which is secreted by mesophilic
bacterium (
Wangia profunda
), as a low cost natural adsorbent for removing
Cd
2+
from aqueous solution. FTIR studies indicated that some functional
groups, such as -OH, -COO and C-O-C, were responsible for metal binding.
The monolayer capacity of exopolysaccharide was 116.28 mg g
-1
.
The capacity of
Eleocharis acicularis
biomass to adsorb Cd
2+
from
aqueous solution was evaluated by Miretzky
et al.
[120]. The maximum
adsorption capacity for Cd
2+
was 33.71 mg g
-1
and the efficiency was higher
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