Growth of Aquincola tertiaricarbonis L108 on the fuel oxygenates methyl tert-butyl ether (MTBE), ethyl tert-butyl ether (ETBE) and tert-amyl methyl ether (TAME), as well as on their main metabolites tert-butyl alcohol (TBA), tert-amyl alcohol (TAA) and 2-hydroxyisobutyrate (2-HIBA) was systematically investigated to characterize the range and rates of oxygenate degradation by this strain. The effective maximum growth rates for MTBE, ETBE and TAME at pH 7 and 30 6C were 0.045 h "1 , 0.06 h "1 and 0.055 h "1, respectively, whereas TAA, TBA and 2-HIBA permitted growth at rates up to 0.08 h , respectively. The experimental growth yields with all these substrates were high. Yields of 0.55 g dry mass (dm) (g MTBE) "1 , 0.53 g dm (g ETBE) "1 , 0.81 g dm (g TAME) , and 3.27 mmol 2-HIBA h "1 g "1. The relatively high rates with TBA, TAA and 2-HIBA indicate that the transformations of these metabolites did not limit the metabolism of MTBE and the related ether compounds. Despite the fact that these metabolites still carry a tertiary carbon atom that is commonly suspected to confer recalcitrance to the ether oxygenates, the transformation rates were in the same range as those with succinate and fructose. With MTBE, strain L108 grew at pHs between 5.5 and 8.0 at near-maximal rate, whereas no growth was found below pH 5.0 and above pH 9.0. The optimum growth temperature was 30 6C, but at 5 6C still about 15 % of the maximum rate remained, whereas no growth occurred at 42 6C. This indicates that MTBE metabolites are valuable substrates and that A. tertiaricarbonis L108 is a good candidate for bioremediation purposes. The possible origin of its exceptional metabolic capability is discussed in terms of the evolution of enzymic activities involved in the conversion of compounds carrying tertiary butyl groups.
INTRODUCTIONMethyl tert-butyl ether (MTBE) and the related compounds ethyl tert-butyl ether (ETBE) and tert-amyl methyl ether (TAME) are widely used as oxygenating compounds in gasoline (Krayer von Krauss & Harremoës, 2001), leading to pollution by unnoticed leakages and accidental spills (Baehr et al., 1999;Klinger et al., 2002; Schmidt et al., 2002;Squillace et al., 1996). They threaten water resources by their unpleasant odour and taste and suspected carcinogenicity (McGregor, 2006). Consequently, much effort is put into studying the environmental fate of these compounds and developing measures against fuel oxygenate pollution. Microbial degradation has been considered in both respects (Deeb et al., 2000;Fayolle et al., 2001;Schmidt et al., 2004). However, MTBE and structurally related compounds were initially found to withstand microbial attack. This was thought to be mainly due to the ether bond in these compounds and the presence of a tertiary carbon atom.Generally, it has proved difficult to isolate strains from enrichment cultures using MTBE as sole carbon and energy source. Attempts for more than 15 years were of limited success. At present, there are only a few strains capable of growing solely on oxygenates. The...