Short communicationTreatment of phenol-contaminated soil by Corynebacterium glutamicum and toxicity removal evaluation
Introduction
Phenols and related compounds, which are high on the list of priority contaminants [1], may interfere with the ecosystem equilibrium and, consequently, may affect biogeochemical pathways of organic matter and nutrient recycling [2]. When phenol, a hydrophobic compound, is released into soil, its mobility becomes more restricted than in an aqueous environment due to its adsorption onto solid surfaces [2], [3]. Currently the primary method for its removal is the use of various biological approaches, so-called bioremediation technologies [4], [5], [6]. Of the techniques available for the removal of phenols from soil, biodegradation by soil bacteria is environmentally friendly and cost-effective [7], [8]. Recently Corynebacterium glutamicum, an industrial soil microorganism important for amino acid production, was reported to assimilate various aromatic compounds [9], [10]. In particular, phenol catabolism by C. glutamicum occurs through the catechol branch of the β-ketoadipate pathway [9], [11]. A previous study using a batch culture system showed C. glutamicum biodegrades phenol and uses it as a carbon source [12].
The aim of this study was to investigate the optimal biodegrading conditions of phenol-contaminated soil in the presence of C. glutamicum. Using Daphnia magna, we performed acute toxicity assays to measure the efficiency of toxicity removal based on the degradation of phenol by C. glutamicum. Degradation was evaluated by measuring the overall toxicity of the degradation byproducts.
Section snippets
Microorganism and culture conditions
C. glutamicum ATCC 13032 (America Type Culture Collection, Manassas, VA) was used for phenol degradation in soil. The inocula were cultured at 30 °C and 150 rpm in Luria-Bertani medium [13].
Biodegradation of phenol in soil
The ability of C. glutamicum to remediate the phenol-contaminated soil sample was investigated by carrying out the biodegradation experiment in soil for three days under indoor laboratory conditions. A bulk soil sample (10 g) was completely sterilized in an autoclave at 121 °C and 15 lb/in.2 for 30 min. Samples (10
Optimal experimental conditions for biodegradation of phenol-contaminated soil
To investigate the culture conditions under which the biodegradative ability of C. glutamicum is optimized, soil spiked at a low phenol concentration (2.12 mM) was measured before and after treatment with C. glutamicum and 1% glucose or 1% yeast extract. Fig. 1 shows the effects of C. glutamicum on phenol degradation in soil samples under several culture conditions. In the control sample (i.e., no bacteria), no phenol degradation was observed after three days. Although C. glutamicum was
Conclusions
We investigated and demonstrated the ability of C. glutamicum to degrade phenol in contaminated soil, which is a serious environmental concern. The results showed that phenol degradation in soil was highly effective under optimized conditions, and that the toxicity of the soil was remarkably removed by treatment with C. glutamicum. Based on the results, we emphasize that our approach may facilitate the environmentally friendly soil remediation of high concentrations of phenol over a short time
Acknowledgement
This study was supported by the Korea Research Foundation Grant funded by the Korean Government (MOEHRD, Basic Research Promotion Fund) (KRF-2008- D00175-I00154). The authors are grateful for their support.
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