2012
DOI: 10.1128/jb.01499-12
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Genome Sequence of Pseudomonas aeruginosa DQ8, an Efficient Degrader of n -Alkanes and Polycyclic Aromatic Hydrocarbons

Abstract: Pseudomonas aeruginosa DQ8, which was isolated from the crude oil polluted soil in the Daqing oilfield of China, can efficiently degrade diesel, crude oil, n-alkanes, and polycyclic aromatic hydrocarbons (PAHs). Here, we present a 6.8-Mb assembly of its genome sequence. We have annotated 23 coding sequences (CDSs) responsible for catabolism of n-alkanes and PAHs.

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Cited by 13 publications
(12 citation statements)
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“…None of the BTEX group was metabolized, however (Zhang et al 2011). Moreover, the genome sequencing of DQ8 showed the presence of an alk cluster, confirming the phenotypic observations (Gai et al 2012). Interestingly, the strain exhibited two diversified, well recognized for various bacteria, enzymatic strategies towards fluorene.…”
Section: Bacteria Able To Metabolize Both N-alkanes and Aromatic Hydrsupporting
confidence: 72%
See 1 more Smart Citation
“…None of the BTEX group was metabolized, however (Zhang et al 2011). Moreover, the genome sequencing of DQ8 showed the presence of an alk cluster, confirming the phenotypic observations (Gai et al 2012). Interestingly, the strain exhibited two diversified, well recognized for various bacteria, enzymatic strategies towards fluorene.…”
Section: Bacteria Able To Metabolize Both N-alkanes and Aromatic Hydrsupporting
confidence: 72%
“…Interestingly, the strain exhibited two diversified, well recognized for various bacteria, enzymatic strategies towards fluorene. It could oxidize the compound via both C9-monooxidation and C3,C4dioxidation (Gai et al 2012). P. aeruginosa strain W10 also preferentially utilized n-C 16 as well as naphthalene, phenanthrene, fluoranthene, and pyrene (Chebbi et al 2017).…”
Section: Bacteria Able To Metabolize Both N-alkanes and Aromatic Hydrmentioning
confidence: 99%
“…Specifically, several Pseudomonas isolates including two species closely associated with 16S rRNA gene sequences detected in this study (P. stuzeri, and P. alcaligenes) have demonstrated abilities to degrade PAHs such as naphthalene and phenanthrene, linear and branched alkanes, and diesel range compounds (Takizawa et al 1994;Ramos et al 1995;Whyte et al 1997;Beal and Betts 2000;Bosch et al 2000;Filonov et al 2000; Barathi and Vasudevan 2001;Tian et al 2003;Yeo et al 2003;Kaczorek et al 2011;Rocha et al 2011;Tang et al 2011;Gai et al 2012;Zhang et al 2012). Pseudomonas was one of the dominant genera encapsulated in gels from Bakken shale wells and reintroduced to flowback fluids in laboratory experiments, which substantially improved organic carbon degradation rates (Aukema et al 2014;Strong et al 2014).…”
Section: Implications For Surface Releasesmentioning
confidence: 70%
“…This ability of bacteria to degrade PAHs is due to a multicomponent enzyme system that generates hydroxylated metabolites followed by a series of reactions to achieve the final mineralization of these compounds (Kanaly and Harayama 2000, Haritash and Kaushik 2009, Zhang et al 2011). In the case of P. aeruginosa, its ability to synthesize rhamnolipids in addition to its oxygenase/dehydrogenase system stands out (Rahman et al 2003, Jouanneau et al 2006, Kumara et al 2006, Zhang et al 2011, Zhao et al 2011, Cao et al 2012, Gai et al 2012. In low and high molecular weight PAHs, the first step of PAH biotransformation performed by some bacteria is the generation of dihydrodiols through their oxygenase activity (Kanaly and Harayama 2000) as it occurs in fish.…”
Section: Introductionmentioning
confidence: 99%