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Phenanthrene biodegradation by halophilic M artelella sp. AD ‐3
Author(s) -
Feng T.c.,
Cui C.z.,
Dong F.,
Feng Y.y.,
Liu Y.d.,
Yang X.m.
Publication year - 2012
Publication title -
journal of applied microbiology
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 0.889
H-Index - 156
eISSN - 1365-2672
pISSN - 1364-5072
DOI - 10.1111/j.1365-2672.2012.05386.x
Subject(s) - phenanthrene , halophile , biodegradation , chemistry , strain (injury) , bacteria , microbial biodegradation , bioremediation , environmental chemistry , biochemistry , organic chemistry , biology , microorganism , genetics , anatomy
Aims To investigate the phenanthrene‐degrading abilities of the halophilic M artelella species AD ‐3 under different conditions and to propose a possible metabolic pathway. Methods and Results Using HPLC and GC ‐ MS analyses, the phenanthrene‐degrading properties of the halophilic strain AD ‐3 and its metabolites were analysed. This isolate efficiently degraded phenanthrene under multiple conditions characterized by different concentrations of phenanthrene (100–400 mg l −1 ), a broad range of salinities (0·1–15%) and varying pH s (6·0–10·0). Phenanthrene (200 mg l −1 ) was completely depleted under 3% salinity and a pH of 9·0 within 6 days. The potential toxicity of phenanthrene and its generated metabolites towards the bacterium V ibrio fischeri was significantly reduced 10 days after the bioassay. On the basis of the identified metabolites, enzyme activities and the utilization of probable intermediates, phenanthrene degradation by strain AD ‐3 was proposed in two distinct routes. In route I, metabolism of phenanthrene was initiated by the dioxygenation at C ‐3,4 via 1‐hydroxy‐2‐naphthoic acid, 1‐naphthol, salicylic acid and gentisic acid. In route II, phenanthrene was metabolized to 9‐phenanthrol and 9,10‐phenanthrenequinone. Further study indicated that strain AD ‐3 exhibited a wide spectrum of substrate utilization including other polycyclic aromatic hydrocarbons ( PAH s). Conclusions The results suggest that strain AD ‐3 possesses a high phenanthrene biodegradability and that the degradation occurs via two routes that remarkably reduce toxicity. Significance and Impact of the Study To the best of our knowledge, this work presents the first report of phenanthrene degradation by a halophilic PAH ‐degrading strain via two routes. In the future, the use of halophilic strain AD ‐3 provides a potential application for efficient PAH ‐contaminated hypersaline field remediation.