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. 2019 Oct 29;202(2):329–342. doi: 10.1007/s00203-019-01749-2

Table 1.

List of most notable genera (containing cultivable species and showing > 1% abundance) detected in the aerobic versus the microaerobic enrichments and their predictable role in petroleum hydrocarbon degradation

Genus Abundance of 16S rDNA sequence reads (%) Documented petroleum hydrocarbon degradation ability References
Aerobic enrichment Microaerobic enrichment
Polaromonas 14 < 0.1 Benzene, toluene, naphthalene, medium-chain alkanes Sun et al. (2010), Xie et al. 2011), Jeon et al. (2004) and Scheps et al. (2011)
Pseudomonas 10.5 11 Alkanes, monoaromatic hydrocarbons, PAHs Whyte et al. 1997) and van Beilen and Funhoff (2007)
Acinetobacter 1.8 66.3 Monoaromatic hydrocarbons, long-chain alkanes Lal and Khanna (1996), Di Cello et al. 1997) and Tani et al. (2001)
Acidovorax 6.7 11 Benzene, phenanthrene, chlorobenzene Nestler et al. (2007), Aburto and Peimbert (2011) and Singleton et al. (2018)
Rhodococcus 5.5 < 0.5 Alkanes, aromatic and heterocyclic compounds, PAHs Larkin et al. (2005)
Janthinobacterium 4 ND NR
Chryseobacterium 2.5 ND Lubricating oil Saimmai et al. (2012)
Sphingobium 2.3 ND Monoaromatic hydrocarbons, straight-chain alkanes, PAHs Maeda et al. (2015), Chaudhary et al. (2017) and Révész et al. (2018)
Variovorax < 0.1 1.9 Benzene, phenanthrene Posman et al. 2017) and Singleton et al. (2018)
Azospirillum 1.6 ND PAHs Gałązka et al. (2012)
Simplicispira < 0.1 1.5 NR
Ottowia 1.4 ND Phenol Felföldi et al. (2010)
Flavobacterium 1.3 < 0.1 Crude oil Rahman et al. (2002)
Massilia 1.1 < 0.1 NR

ND not detected, NR not reported