Sorption of Cadmium and Lead by Bacteria-Ferrihydrite Composites
The sorptive behavior of bacteria-iron oxide composites was investigated in batch metal sorption assays using ferrihydrite in isolation (0.13 and 0.14 g/L ferrihydrite in cadmium and lead systems, respectively) as well as in combination with Bacillus subtilis (0.25 g/L adsorbent mixture) and Escheri...
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Veröffentlicht in: | Geomicrobiology journal 2005-09, Vol.22 (6), p.299-310 |
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Sprache: | eng |
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Zusammenfassung: | The sorptive behavior of bacteria-iron oxide composites was investigated in batch metal sorption assays using ferrihydrite in isolation (0.13 and 0.14 g/L ferrihydrite in cadmium and lead systems, respectively) as well as in combination with Bacillus subtilis (0.25 g/L adsorbent mixture) and Escherichia coli (0.27 g/L adsorbent mixture). A pH range from 3.0 to 6.5 was studied using total metal concentrations of
1.0 × 10
− 4.0
and 3.2
×
10
− 5
M with adsorbent mixtures proportioned on a 1:1 mass/volume basis. The log of the apparent surface complex formation constants (log K
S
M
) and sorption capacity (S
max
) values were determined by fitting the experimental data to one-site Langmuir sorption isotherms. The one-site model effectively described the sorption data (r
2
>
0.9), where Cd
2 +
exhibited somewhat lower sorption affinities (log K
S
M
=
−3
for ferrihydrite,
−1.7
for B. subtilis-ferrihydrite, and −1.1 for E. coli-ferrihydrite) than Pb
2 +
(log K
S
M
= −0.9 for ferrihydrite,
−
0.2 forB. subtilis-ferrihydrite, and -0.1 for E. coli-ferrihydrite). The corresponding S
max
values for Cd
2 +
and Pb
2 +
on ferrihydrite were 0.78 mmole/g and 1.34 mmole/g, respectively. For the B. subtilis-ferrihydrite composites, Cd
2 +
and Pb
2 +
S
max
values were lower at 0.29 mmole/g and 0.5 mmole/g, respectively. Similar values were determined for the E. coli-ferrihydrite composites (0.15 mmole/g and 0.68 mmole/g for Cd
2 +
and Pb
2 +
, respectively). The sorption of Cd
2 +
and Pb
2 +
by each of the sorbent systems exhibited a strong dependence on pH with sorption edges in the range of pH 4.0 to 7.3. The observed S
max
of the composites were lower than values predicted upon available site additivity (Cd
2 +
B. subtilis −ferrihydrite
: 0.29 mmole/g (observed) < 0.57 mmole/g (calculated); Cd
2 +
E. coli −ferrihydrite
: 0.15 mmole/g (observed) < 0.44 mmole/ g (calculated); Pb
2 +
B. subtilis −ferrihydrite
: 0.5 mmole/g (observed) < 0.805 mmole/g (calculated); Pb
2 +
E. coli -ferrihydrite
: 0.68 mmole/g (observed) < 0.775 mmole/g (calculated)), implying that a masking of reactive surface sites by attachment had occurred between the bacteria and ferrihydrite. Electrophoretic mobility analysis indicated that the ferrihydrite surface properties dominate the net surface charge for each composite system with lesser contributions from the bacteria. |
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ISSN: | 0149-0451 1521-0529 |
DOI: | 10.1080/01490450500184694 |