2013
DOI: 10.1371/journal.pone.0082397
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Biochemical, Transcriptional and Translational Evidences of the Phenol-meta-Degradation Pathway by the Hyperthermophilic Sulfolobus solfataricus 98/2

Abstract: Phenol is a widespread pollutant and a model molecule to study the biodegradation of monoaromatic compounds. After a first oxidation step leading to catechol in mesophilic and thermophilic microorganisms, two main routes have been identified depending on the cleavage of the aromatic ring: ortho involving a catechol 1,2 dioxygenase (C12D) and meta involving a catechol 2,3 dioxygenase (C23D). Our work aimed at elucidating the phenol-degradation pathway in the hyperthermophilic archaea Sulfolobus solfataricus 98/… Show more

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Cited by 19 publications
(17 citation statements)
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“…Separation was achieved with an LC column Waters XTerra C18 column, eluted with a gradient of acetonitrile in water containing acetic acid (0.1% v/v); from 0 to 40% acetonitrile, using the following parameters-ionization: electro spray positive (ES+), low rate: 0.15 ml/min. For mass spectrometer, the following parameters were used: desolvation gas: 550 L/h; cone gas: 30 L/h; desolvation temperature: 250°C; source temperature: 110˚C; capillary voltage: 3000 V; cone voltage: 30 V; collision energy: 4 eV; nebulize gas: nitrogen 30 ml/min; collision gas: argon 0.5 µl /min (Comte et al, 2013;and Glish and Vachet, 2003).…”
Section: Phenol Estimation By Analytical Methods and Lc-ms Analysismentioning
confidence: 99%
“…Separation was achieved with an LC column Waters XTerra C18 column, eluted with a gradient of acetonitrile in water containing acetic acid (0.1% v/v); from 0 to 40% acetonitrile, using the following parameters-ionization: electro spray positive (ES+), low rate: 0.15 ml/min. For mass spectrometer, the following parameters were used: desolvation gas: 550 L/h; cone gas: 30 L/h; desolvation temperature: 250°C; source temperature: 110˚C; capillary voltage: 3000 V; cone voltage: 30 V; collision energy: 4 eV; nebulize gas: nitrogen 30 ml/min; collision gas: argon 0.5 µl /min (Comte et al, 2013;and Glish and Vachet, 2003).…”
Section: Phenol Estimation By Analytical Methods and Lc-ms Analysismentioning
confidence: 99%
“…Most microorganisms usually degrade phenol through the aerobic pathway in which the phenol hydroxylase catalyzes phenol to catechol, which is the first and key step of phenol degradation and often directly affects the degradation rate of phenol. Then, this pathway can be divided into the ortho-pathway and meta-pathway, which are two separate metabolic systems according to the opening mode of the aromatic ring[ 38 , 39 ]. Interestingly, different kinds and even concentrations of aromatic hydrocarbons can activate different metabolic pathways of some certain microorganisms, with Pseudomonas cepacia as an example in which salicylate can only activate the ortho-pathway while benzoate can activate both the ortho-pathway and meta-pathway[ 40 , 41 ].…”
Section: Discussionmentioning
confidence: 99%
“…Genomic sequencing of Sulfolobus solfataricus st. P2 found genes for aromatic degradation and it was found to be able to degrade phenol aerobically through meta -ring cleavage [ 58 ]. A strain of the closely related thermophilic Sulfolobus solfataricus st. 98/2 was later found to be able to degrade phenol at 80°C and 3.2 pH [ 59 , 60 ] through meta -ring cleavage also [ 61 ]. A dienelactone hydrolase from Sulfolobus solfataricus st. P1 was also identified and characterized [ 62 ].…”
Section: Degradation Of Organics With Thermophilic Sulfomentioning
confidence: 99%