Short Genome CommunicationsComplete genome sequence of Novosphingobium resinovorum SA1, a versatile xenobiotic-degrading bacterium capable of utilizing sulfanilic acid
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Funding
Supported by the European Union and co-financed by the European Social Fund (grant agreement no. TÁMOP-4.2.2.B-15/1/KONV-2015-0006) and by the Norway Grant (grant agreement no. HU09-0044-A1-2013).
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Cited by (18)
Characteristics and functional analysis of the secondary chromosome and plasmids in sphingomonad
2022, International Biodeterioration and BiodegradationCitation Excerpt :Most of the plasmids are circular, while a few plasmids are not circularized successfully based on genome sequencing data, such as the plasmid pSF4 of Sphingobium fuliginis ATCC 27551 (Azam et al., 2019), pRSM4 of Sphingobium sp. RSMS (Rangu et al., 2020), and pSA1 of Novosphingobium resinovorum SA1 (Hegedus et al., 2017), probably due to linear structures or the lack of short but not amplifiable sequences. The plasmid sizes range from 4.3 Kb to 1161.6 Kb, and 49.5% plasmids belong to megaplasmids which are larger than 100 Kb (Fig. 1b).
Bibliometric analysis of microbial sulfonamide degradation: Development, hotspots and trend directions
2022, ChemosphereCitation Excerpt :At present, there are many studies on microbial sulfonamides degradation (MSD), including single and mixed microorganism systems. Research on single microorganism systems have been mainly conducted in the laboratory and focused on the degradation ability and survival conditions of the microorganisms, as well as the degradation kinetics and pathway of sulfonamides (Deng et al., 2016; Hegedus et al., 2017; Jiang et al., 2014; Liang et al., 2021a). However, the mechanism for microbial degradation is still unclear, particularly the functional enzymes and genes involved in the degradation process.
Plasmid-mediated catabolism for the removal of xenobiotics from the environment
2021, Journal of Hazardous MaterialsCitation Excerpt :The catabolic genes responsible for degradation are located in the mega-plasmid designated pSWIT02 in RW1. The genomic analysis of the Novosphingobium resinovorum SA1 found it to be capable of bio-converting sulfanilic acid and various other aromatic compounds (Shintani et al., 2015; Urata et al., 2006; Botond et al., 2017). The genome sequence revealed that the degradation pathway is scattered over multiple plasmids.
Enhanced degradation of 4-aminobenzenesulfonate by a co-culture of Afipia sp. 624S and Diaphorobacter sp. 624L
2021, Journal of Bioscience and BioengineeringA data-independent acquisition approach based on HRMS to explore the biodegradation process of organic micropollutants involved in a biological ion-exchange drinking water filter
2021, ChemosphereCitation Excerpt :According to the literature, bacteria in the genus Novosphingobium associated with the biodegradation of carbon substrates are prevalent in environments such as lakes and soils and actively participate in the biodegradation process of MC-LR (Jiang et al., 2011; Wang et al., 2018). Several articles also mention that this bacterial genus is involved in the biodegradation of xenobiotic compounds containing an aromatic structure such as atrazine and venlafaxine (Dai et al., 2015; Hegedűs et al., 2017). Fang et al. stated that Bradyrhizobium, can harbor the atzA gene which is involved in the dechlorination of atrazine to form hydroxyatrazine (present at 500 ng·L-1 in the culture aliquots) which is consistent with what we measured in the culture aliquots (Fang et al., 2015).