2015
DOI: 10.1016/j.ibiod.2015.06.008
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Phenanthrene biodegradation by sphingomonads and its application in the contaminated soils and sediments: A review

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Cited by 151 publications
(47 citation statements)
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“…Microbial degradation of phenanthrene can proceed by three different methods: mineralization, co-metabolic transformation and oxidation. In the case of aerobic growth of sphingomonads, oxidation is the favored mechanism of phenathrene degradation (Waigi et al, 2015 ). As with other PAHs, aerobic degradation of phenanthrene is initiated by the addition of two oxygen atoms to the aromatic ring, an event that is catalyzed by an aromatic-ring dioxygenase (Figure 5A ).…”
Section: Resultsmentioning
confidence: 99%
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“…Microbial degradation of phenanthrene can proceed by three different methods: mineralization, co-metabolic transformation and oxidation. In the case of aerobic growth of sphingomonads, oxidation is the favored mechanism of phenathrene degradation (Waigi et al, 2015 ). As with other PAHs, aerobic degradation of phenanthrene is initiated by the addition of two oxygen atoms to the aromatic ring, an event that is catalyzed by an aromatic-ring dioxygenase (Figure 5A ).…”
Section: Resultsmentioning
confidence: 99%
“…This metabolite can be further degraded by two different routes: it can be processed by dioxygenases and dehydrogenases ( ortho -cleavage route) to generate o -phtalate, which is later metabolized through protocatechuate to generate tricarboxylic acid (TCA) intermediates (Figure 5 , steps 8A to 16A). Alternatively, by the meta -cleavage route, 1-hydroxy-2-naphtoic acid is decarboxylated to generate 1,2-dihydroxinaphtalene, which is further serially processed by dioxygenase, isomerase, aldolase, and dehydrogenase activities to produce salicylic acid (Figure 5 , steps 8B to 12B; Goyal and Zylstra, 1997 ; Waigi et al, 2015 ). Salicylic acid is then further processed through gentisate (steps 13C to 16C) or catechol pathways (steps 13B to 18B), to generate TCA cycle intermediates, with the catechol pathway generating the yellow colored hydroximuconic acid used for the qualitative selection of strains in our screening approach.…”
Section: Resultsmentioning
confidence: 99%
“…This is concordant with previous results on PHE-spiked agricultural soils, where Sphingomonas became the dominant genus within 2 months, together with a significant increase in Phenylobacterium abundance compared to unspiked controls (Ding et al, 2012 ). Sphingomonads are known as active hydrocarbon degraders (Peng et al, 2008 ), often isolated from polluted sites and able to use PHE and other PAHs as sole carbon sources (reviewed in Waigi et al, 2015 ). In general, sphingomonads feature several adaptive strategies for efficient PAH degradation in oligotrophic environments, such as: (i) adhesion to hydrophobic substrates and formation of biofilm (Johnsen and Karlson, 2004 ); (ii) the presence of glycosphingolipids in their cell envelope (Kawahara et al, 1999 ), which are more hydrophobic than common membrane lipids found in other Gram-negative bacteria; and (iii) high affinity uptake systems for recalcitrant compounds (Peng et al, 2008 ).…”
Section: Discussionmentioning
confidence: 99%
“…Microbial degradation or mineralization depends on the metabolic potential of microorganisms to detoxify or transform these pollutants. Several enzyme-catalyzed metabolic reactions in the biodegradation process include the addition of oxygen to double bonds, dehalogenation, ring cleavage, and the addition of hydroxyl groups to the benzene ring (17)(18)(19). Some functional genes have been identified and linked to the initial metabolic process of PAH and PCB degradation, including PAH ring-hydroxylating dioxygenase (PAH-RHD) (20) and biphenyl dioxygenase (bphA) genes (11).…”
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confidence: 99%