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. 2020 Feb 22:14:5.
doi: 10.1186/s13036-020-0229-5. eCollection 2020.

Biodegradation of penicillin G from industrial bacteria residue by immobilized cells of Paracoccus sp. KDSPL-02 through continuous expanded bed adsorption bioreactor

Affiliations

Biodegradation of penicillin G from industrial bacteria residue by immobilized cells of Paracoccus sp. KDSPL-02 through continuous expanded bed adsorption bioreactor

Peng Wang et al. J Biol Eng. .

Abstract

Background: An efficient biodegradation-strengthening approach was developed to improve penicillin G degradation from industrial bacterial residue in an expanded bed adsorption bioreactor (EBAB) is reported in this paper.

Results: Paracoccus sp. strain KDSPL-02 was isolated based on its ability to use penicillin G as the sole carbon and nitrogen source. Strain identification was based on analyses of morphology, physio-biochemical characteristics, and 16S rDNA sequences. The effects of temperature, pH, PVA-sodium alginate concentration, calcium chloride concentration and initial penicillin G concentration were investigated. Repeated operations of immobilized cells with EBAB, At initial penicillin concentrations below 2.0 g L- 1, the continuous mode could reach more than 20 times, and the degradation rate reached 100%.

Conclusions: The present study suggests that the EBAB system can be utilized for the simple and economical biodegradation of penicillin G from industrial bacterial residue.

Keywords: Expanded bed adsorption bioreactor; Immolilization; Paracoccus sp.; Penicillin G.

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Conflict of interest statement

Competing interestsThe authors declare that they have no competing interests.

Figures

Fig. 1
Fig. 1
Schematic dragram of the EBAB system used in penicillin G biodegradation
Fig. 2
Fig. 2
Phylogenetic analysis of the strain KDSPL-02 related species by the neighbour-joining approach. The scale bars represent 0.005 substitutions per site
Fig. 3
Fig. 3
The influence of temperature on the degradation activity of free and immobized KDSPL-02 cell. (black square refers free cells, red circle refers immobilized cells)
Fig. 4
Fig. 4
Effect of pH on the degradation ability of the immobilized KDSPL-02. (black triangle refers free cells, red circle refers immobilized cells)
Fig. 5
Fig. 5
Effect of support materials and cross-linking solution concentration on the formation of immobilized beads. a Effect of PVA concentration on the formation of immobilized beads (black square refers 2.0% PVA, red circle refers 2.5% PVA, blue up triangle refers 3.0% PVA, green down triangle refers 3.5% PVA, pink left triangle refers 4.0% PVA); b Effect of calcium chloride concentration on the formation of immobilized beads (black square refers 1.8% calcium chloride, red circle refers 2.0% calcium chloride, blue triangle refers 2.2% calcium chloride); c Effect of sodium alginate concentration on the formation of immobilized beads (black square refers 2.0% sodium alginate, red circle refers 2.5% sodium alginate, blue up triangle refers 3.0% sodium alginate, green down triangle refers 3.5% sodium alginate, pink left triangle refers 4.0% sodium alginate)
Fig. 6
Fig. 6
Degradation of free and immobilized cells with different initial concentrations of Penicillin G. (black square refers 1.6 g/L immobilized cells, red circle refers 1.6 g/L free cells, blue up triangle refers 1.2 g/L immobilized cells, green down triangle refers 1.2 g/L free cells)
Fig. 7
Fig. 7
Repeated batch Penicillin G biodegradation in EBAB system. Biodegradation conditions: 30 °C, pH 7.0, 3.0% sodium alginate, 3.0% PVA and 2.0% calcium chloride. Initial Penicillin G concentration was 1.2 g L−1
Fig. 8
Fig. 8
Penicillin G degradation activity of clear liquid and crude liquid in expanded bed reactor. (black square refers clear liquid, red circle refers crude liquid)

References

    1. Akmehmet Balcıoğlu I, Ötker M. Treatment of pharmaceutical wastewater containing antibiotics by O3 and O3/H2O2 processes. Chemosphere. 2003;50(1):85–95. doi: 10.1016/S0045-6535(02)00534-9. - DOI - PubMed
    1. Arslan-Alaton I, Dogruel S. Pre-treatment of penicillin formulation effluent by advanced oxidation processes. J Hazard Mater. 2004;112(1–2):105–113. doi: 10.1016/j.jhazmat.2004.04.009. - DOI - PubMed
    1. Bergero MF, Lucchesi GI. Immobilization of Pseudomonas putida a (ATCC 12633) cells: a promising tool for effective degradation of quaternary ammonium compounds in industrial effluents. Int Biodeterior Biodegradation. 2015;100:38–43. doi: 10.1016/j.ibiod.2015.02.004. - DOI
    1. Chen D, Chen J, Zhong W, Cheng Z. Degradation of methyl tert-butyl ether by gel immobilized Methylibium petroleiphilum PM1. Bioresour Technol. 2008;99(11):4702–4708. doi: 10.1016/j.biortech.2007.09.075. - DOI - PubMed
    1. Chen K-C, Chen C-Y, Peng J-W, Houng J-Y. Real-time control of an immobilized-cell reactor for wastewater treatment using ORP. Water Res. 2002;36(1):230–238. doi: 10.1016/S0043-1354(01)00201-9. - DOI - PubMed

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