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
. 2023 Sep 13:14:1227210.
doi: 10.3389/fmicb.2023.1227210. eCollection 2023.

Enhanced biodegradation of phenanthrene and anthracene using a microalgal-bacterial consortium

Affiliations

Enhanced biodegradation of phenanthrene and anthracene using a microalgal-bacterial consortium

Mubasher Zahir Hoque et al. Front Microbiol. .

Erratum in

Abstract

Polycyclic aromatic hydrocarbons (PAHs) are chemicals that are released into the environment during activities of the petroleum industry. The bioaccumulation, carcinogenic and mutagenic potential of PAHs necessitates the bioremediation of these contaminants. However, bioremediation of PAHs has a number of limitations including the inability of a single microbe to degrade all of the PAH fraction's environmental constituents. Therefore, a different paradigm, employing microalgal-bacterial consortium (MBC), may be used to effectively remove PAHs contaminants. In this type of interaction, the microalgae and bacteria species in the consortium work together in a way that enhances the overall performance of the MBC. Bacterial species in the consortium provide essential nutrients or growth factors by degrading toxic substances and provide these to microalgae, while the microalgae species provide organic carbon for the bacterial species to grow. For the first time, the ability of Gonium pectorale (G. pectorale) microalgae to break down phenanthrene (PHE) and anthracene (ANT) was investigated. Phenanthrene was shown to be more effectively degraded by G. pectorale (98%) as compared to Bacillus licheniformis (B. licheniformis) 19%. Similarly, G. pectorale has effectively degrade anthracene (98%) as compared with B. licheniformis (45%). The consortia of G. pectorale and B. licheniformis has shown a slight increase in the degradation of PHE (96%) and ANT (99%). Our findings show that B. licheniformis did not inhibit the growth of G. pectorale and in the consortia has effectively eliminated the PAHs from the media. Therefore G. pectorale has a tremendous potential to remove PAHs from the polluted environment. Future research will be conducted to assess Gonium's capacity to eliminate PAHs that exhibit high molar masses than that of PHE and ANT.

Keywords: Gonium pectorale; biodegradation genes; microalgal-bacterial consortium; petrogenic pollutants; phenanthrene and anthracene; polycyclic aromatic hydrocarbons; water contaminants.

PubMed Disclaimer

Conflict of interest statement

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Figures

Figure 1
Figure 1
Growth curve of G. pectorale without any PHE and ANT. (A) Growth curve of G. pectorale alone. (B) Growth curve for G. pectorale in consortia.
Figure 2
Figure 2
Growth curve of B. licheniformis without any PHE and ANT. (A) Growth curve of B. licheniformis alone. (B) Growth curve for B. licheniformis in consortia.
Figure 3
Figure 3
Overview of PHE and ANT degradation by individual strains and in consortia.
Figure 4
Figure 4
Proposed metabolic pathways for degradation of PHE (A) and ANT (B) using Gonium pectorale.
Figure 5
Figure 5
AP2 family transcription factor binding sites in the promoter sequences of the G. pectorale carboxymethylenebutenolidases. (A) Occurrence of the transcription factor binding sites (orange: negative strand, pink: positive strand); (B) Consensus transcription factor binding sequence found.

References

    1. Abdel-Shafy H. I., Mansour M. S. (2016). A review on polycyclic aromatic hydrocarbons: source, environmental impact, effect on human health and remediation. Egypt. J. Pet. 25, 107–123. doi: 10.1016/j.ejpe.2015.03.011 - DOI
    1. Adeniji A., Okoh O., Okoh A. (2019). Levels of polycyclic aromatic hydrocarbons in the water and sediment of Buffalo River estuary, South Africa and their health risk assessment. Arch. Environ. Con. Tox. 76, 657–669. doi: 10.1007/s00244-019-00617-w, PMID: - DOI - PMC - PubMed
    1. Ahmad I. (2021). Microalgae–Bacteria consortia: a review on the degradation of polycyclic aromatic hydrocarbons (PAHs). Arab. J. Sci. Eng. 47, 19–43. doi: 10.1007/s13369-021-06236-9 - DOI
    1. Alvarez-Ospina H., Giordano S., Ladino L. A., Raga G. B., Muñoz-Salazar J. I., Leyte-Lugo M., et al. . (2021). Particle-bound polycyclic aromatic hydrocarbons (pPAHs) in Merida, Mexico. Aerosol Air Qual. Res. 21:200245. doi: 10.4209/aaqr.200245 - DOI
    1. Boduroğlu G., Kılıç N. K., Dönmez G. (2014). Bioremoval of reactive blue 220 by Gonium sp. biomass. Environ. Technol. 35, 2410–2415. doi: 10.1080/09593330.2014.908240, PMID: - DOI - PubMed

LinkOut - more resources