Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2015 Oct 27;10(10):e0140962.
doi: 10.1371/journal.pone.0140962. eCollection 2015.

Biosorption of Cadmium and Manganese Using Free Cells of Klebsiella sp. Isolated from Waste Water

Affiliations

Biosorption of Cadmium and Manganese Using Free Cells of Klebsiella sp. Isolated from Waste Water

Yunnan Hou et al. PLoS One. .

Erratum in

Abstract

In the present study, we evaluated a bacterium that was isolated from waste water for its ability to take up cadmium and manganese. The strain, identified both biochemically and by its 16S rRNA gene sequence as Klebsiella, was named Yangling I2 and was found to be highly resistant to heavy metals. Surface characterization of the bacterium via SEM revealed gross morphological changes, with cells appearing as biconcave discs after metal exposure rather than their typical rod shape. The effects of pH, temperature, heavy metal concentration, agitation and biomass concentration on the uptake of Cd(II) and Mn(II) was measured using atomic absorption spectrophotometry. The results showed that the biosorption was most affected by pH and incubation temperature, being maximized at pH 5.0 and 30°C, with absorption capacities of 170.4 and 114.1 mg/g for Cd(II) and Mn(II), respectively. Two models were investigated to compare the cells' capacity for the biosorption of Cd and Mn, and the Langmuir model based on fuzzy linear regression was found to be close to the observed absorption curves and yield binding constants of 0.98 and 0.86 for Cd and Mn, respectively. This strain of Klebsiella has approximately ten times the absorption capacity reported for other strains and is promising for the removal of heavy metals from waste water.

PubMed Disclaimer

Conflict of interest statement

Competing Interests: The authors have declared that no competing interests exist.

Figures

Fig 1
Fig 1. The growth curves of Klebsiella sp. Yangling I2 in the presence of different initial concentrations of Cd(II).
Initial pH = 5.0, biomass concentration = 1.0 g/L, and contact time = 26 h.
Fig 2
Fig 2. The growth curves of Klebsiella sp. Yangling I2 in the presence of different initial concentrations of Mn(II).
Initial pH = 5.0, biomass concentration = 1.0 g/L, and contact time = 26 h.
Fig 3
Fig 3
(A) SEM images of Klebsiella sp. Yangling I2, (B) Klebsiella sp. Yangling I2 equilibrated with 4mM Cd(II), and (C) Klebsiella sp. Yangling I2 equilibrated with 20mM Mn(II).
Fig 4
Fig 4. Effect of pH on the absorption of Cd(II) by Klebsiella sp. Yangling I2.
Initial ion concentration = 2 mM, biomass concentration = 1.0 g/L, and contact time = 26 h.
Fig 5
Fig 5. Effect of pH on the absorption of Mn(II) by Klebsiella sp. Yangling I2.
Initial ion concentration = 10 mM, biomass concentration = 1.0 g/L, and contact time = 20 h.
Fig 6
Fig 6. Effect of incubation temperature on the absorption of Cd(II) by Klebsiella sp. Yangling I2.
Initial ion concentration = 10 mM, initial pH = 5.0, and contact time = 26 h.
Fig 7
Fig 7. Effect of incubation temperature on the absorption of Mn(II) by Klebsiella sp. Yangling I2.
Initial ion concentration = 10 mM, initial pH = 5.0, and contact time = 20 h.
Fig 8
Fig 8. Effect of initial ion concentration on the absorption of Cd(II) by Klebsiella sp. Yangling I2.
Initial pH = 5.5, biomass concentration = 1.0 g/L, and contact time = 26 h.
Fig 9
Fig 9. Effect of initial ion concentration on the absorption of Mn(II) by Klebsiella sp. Yangling I2.
Initial pH = 5.0, biomass concentration = 1.0 g/L, and contact time = 20 h.
Fig 10
Fig 10. Effect of agitation speed on the absorption of Cd(II) by Klebsiella sp. Yangling I2.
Initial ion concentration = 2 mM, initial pH = 5.5, and contact time = 26 h.
Fig 11
Fig 11. Effect of agitation speed on the absorption of Mn(II) by Klebsiella sp. Yangling I2.
Initial ion concentration = 10 mM, initial pH = 5.0, and contact time = 20 h.
Fig 12
Fig 12. Effect of biosorbent density on the absorption of Cd(II) by Klebsiella sp. Yangling I2.
Initial ion concentration = 2 mM, initial pH = 5.5, and contact time = 26 h.
Fig 13
Fig 13. Effect of biosorbent density on the absorption of Mn(II) by Klebsiella sp. Yangling I2.
Initial ion concentration = 10 mM, initial pH = 5.0, and contact time = 20 h.
Fig 14
Fig 14. Effect of contact time on the uptake of Cd(II) and Mn(II) by Klebsiella sp. Yangling I2.
Fig 15
Fig 15. (A) Langmuir isotherm based on fuzzy linear regression for the absorption of cadmium. (B) Langmuir isotherm based on fuzzy linear regression for the absorption of manganese. (C) Freundlich isotherm based on fuzzy linear regression for the absorption of cadmium. (D) Freundlich isotherm based on fuzzy linear regression for the absorption of manganese.

Similar articles

Cited by

References

    1. Wang JL, Chen C (2006) Biosorption of heavy metals by Saccharomyces cerevisiae: A review. Biotechnology Advances 24: 427–451. - PubMed
    1. Buxbaum G (2008) Industrial inorganic pigments: John Wiley & Sons.
    1. Scoullos M (2001) Mercury, cadmium, lead: Handbook for sustainable heavy metals policy and regulation: Springer.
    1. Benguella B, Benaissa H (2002) Cadmium removal from aqueous solutions by chitin: kinetic and equilibrium studies. Water Research 36: 2463–2474. - PubMed
    1. Yin J, Blanch HW (1989) A bio-mimetic cadmium adsorbent: Design, synthesis, and characterization. Biotechnology and Bioengineering 34: 180–188. - PubMed

Publication types

LinkOut - more resources