1). Of the above, two isolates (Acinetobacter sp. and A. xylosoxidans 2) displayed appreciable growth on C19–C21 alkanes, and hence probably represented more generalist degraders. For long-chain degradation one isolate consistently displayed a higher affinity for long-chain length over mid-chain length (Pseudomonas Epacadostat supplier anguilliseptica), again indicating probable compartmentalization of physiologies within the community. Of the remaining five isolates only low growth on all substrates was observed across a range of chain lengths, suggesting

that these strains were generalist degraders with a relatively low degradation capability and low specialization. Interestingly, no degrader displayed a large growth capability on C18 or naphthalene as a sole carbon source. Despite a single carbon chain length difference between C17 and C19, C18 degradation seemed to be problematic, even for organisms that grew well on either mid- or long-chain alkanes. The same was true for naphthalene. Lack of naphthalene degradation could be explained by its higher toxicity, due to its relatively high solubility of 30 mg L−1 (Atlas, 1981; Bouchez et al.,

1995), as well as previous reports of naphthalene degraders being Selleckchem PD 332991 recalcitrant to culture (Huang et al., 2009). However, the compound’s degradation (Cerniglia, 1984; Gibson & Subramanian, 1984; Yu & Chu, 2005) and the isolation of organisms that utilize it is well documented (Cerniglia & Shuttleworth, 2002). The lack of naphthalene-degrading isolates may also be an artefact of the isolation method, which did not select for them specifically at such high concentration. In the case of C18 degradation, previous studies have reported both efficient and slow degradation rates by individual organisms and microbial consortia (Abed et al., 2002; Grotzschel et al., 2002; Radwan et al., 2002). In the present study, the results suggest that C18n-alkanes and naphthalene are more than likely remediated at low levels

by a range of organisms overlapping in their abilities in situ. This hypothesis is supported by the GC-MS analysis of the site diesel fuel, which showed C18n-alkanes to be Benzatropine the overall most abundant constituents and naphthalene the most abundant aromatic compound (Fig. 1). At this stage, it is important to consider the bioavailability of the 10 compounds for microbial utilization. The compounds were added to media at a relatively high concentration of 1000 p.p.m. (or 1 g L−1) in order to mimic the concentration of diesel fuel at the study site. In reality, however, only a fraction of the hydrocarbon added would have been available to the organisms. The water solubility of mid- to long-chain length alkanes is notoriously difficult to measure as well as predict. A number of studies have estimated the solubility of C13–C21 alkanes to range between a mole fraction value of 4 × 10−10 and 7 × 10−11 at 25 °C (Sutton & Calder, 1974; Ferguson et al., 2009).