Abstract

Biodegradation of phenol using bacteria is recognized as an efficient, environmentally friendly and cost-effective approach for reducing phenol pollutants compared to the current conventional physicochemical processes adopted. A potential phenol degrading bacterial strain Glutamicibacter nicotianae MSSRFPD35 was isolated and identified from Canna indica rhizosphere grown in distillery effluent contaminated sites. It showed high phenol degrading efficiency up to 1117 mg L–1 within 60 h by the secretion of catechol 1,2-dioxygenase via ortho intradial pathway. The strain MSSRFPD35 possess both the catechol 1,2 dioxygenase and catechol 2,3 dioxygenase coding genes that drive the ortho and meta pathways, but the enzymatic assay revealed that the strain cleaves catechol via ortho pathway. Haldane’s kinetic method was well fit to exponential growth data and the following kinetic parameter was obtained: μ∗ = 0.574 h–1, Ki = 268.1, Ks = 20.29 mg L–1. The true μmax and Sm were calculated as 0.37 h–1 and 73.76 mg L–1, respectively. The Haldane’s constant values were similar to earlier studies and healthy fitness depicted in correlation coefficient value R2 of 0.98. Phenol degrading kinetic’s was predicted using Haldane’s model as qmax 0.983, Ki′ 517.5 and Ks′ 9.152. Further, MSSRFPD35 was capable of utilizing different monocyclic and polycyclic aromatic hydrocarbons and to degrade phenol in the presence of different heavy metals. This study for the first time reports high phenol degrading efficiency of G. nicotianae MSSRFPD35 in the presence of toxic heavy metals. Thus, the strain G. nicotianae MSSRFPD35 can be exploited for the bioremediation of phenol and its derivatives polluted environments, co-contaminated with heavy metals.

Highlights

  • Phenol and its derivatives namely nitrophenol, halogenated phenol, alkylphenol, etc. are widely used in several industrial plants like petrochemical, phenol resin, pharmaceuticals, paint, textile, leather, pulp mills, coal conversion, and leather processing units (Haddadi and Shavandi, 2013; Jiang et al, 2013; Villegas et al, 2016; Prasse et al, 2018)

  • The enriched Canna indica rhizosphere soil suspension spread plated on Davis minimal medium (DMM) agar medium amended with 200 mg L−1 of phenol yielded 7.3 log10 colonyforming units (CFU) ml−1 after 48 h of incubation at 30◦C

  • Around 128 different morphotype bacterial colonies were isolated and the phenol tolerance assay revealed that 11 isolates which were the most dominant colonies could grow in 1000 mg L−1 of phenol concentration and were coded as MSSRFPD27, MSSRFPD28, MSSRFPD29, MSSRFPD30, MSSRFPD35, MSSRFPD36, MSSRFPH100, MSSRFPH124, MSSRFPH134, MSSRFPH139, and MSSRFPH145

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Summary

Introduction

Phenol and its derivatives namely nitrophenol, halogenated phenol, alkylphenol, etc. are widely used in several industrial plants like petrochemical, phenol resin, pharmaceuticals, paint, textile, leather, pulp mills, coal conversion, and leather processing units (Haddadi and Shavandi, 2013; Jiang et al, 2013; Villegas et al, 2016; Prasse et al, 2018). Phenol is highly soluble in water up to the concentration of 10 g L−1 (Bajaj et al, 2009) and the effluents discharged from industries contain high concentrations of phenol and its derivatives in the range of 50–2000 mg L−1 (Jusoh and Razali, 2008) concentrations much higher than the permissible limits leading to high risk of polluting the environment. The effluent released from industries contain heavy metals like copper, lead, cadmium, chromium, etc., as co-contaminants in different composition and concentration which are highly toxic, persistent, and non-degradable in nature (Thavamani et al, 2012; Wong et al, 2015). It is imperative to reduce the concentration of phenol and heavy metals in the industrial effluents and maintain defined standards before releasing these pollutants into the environment

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