cCupriavidus pinatubonensis JMP134, like many other environmental bacteria, uses a range of aromatic compounds as carbon sources. Previous reports have shown a preference for benzoate when this bacterium grows on binary mixtures composed of this aromatic compound and 4-hydroxybenzoate or phenol. However, this observation has not been extended to other aromatic mixtures resembling a more archetypal context. We carried out a systematic study on the substrate preference of C. pinatubonensis JMP134 growing on representative aromatic compounds channeled through different catabolic pathways described in aerobic bacteria. Growth tests of nearly the entire set of binary combinations and in mixtures composed of 5 or 6 aromatic components showed that benzoate and phenol were always the preferred and deferred growth substrates, respectively. This pattern was supported by kinetic analyses that showed shorter times to initiate consumption of benzoate in aromatic compound mixtures. Gene expression analysis by real-time reverse transcription-PCR (RT-PCR) showed that, in all mixtures, the repression by benzoate over other catabolic pathways was exerted mainly at the transcriptional level. Additionally, inhibition of benzoate catabolism suggests that its multiple repressive actions are not mediated by a sole mechanism, as suggested by dissimilar requirements of benzoate degradation for effective repression in different aromatic compound mixtures. The hegemonic preference for benzoate over multiple aromatic carbon sources is not explained on the basis of growth rate and/or biomass yield on each single substrate or by obvious chemical or metabolic properties of these aromatic compounds.A romatic compounds (AC) are widespread in the environment, displaying a heterogeneous structural diversity. They can be naturally originated by biotic and abiotic processes or released as pollutants into the environment. AC primarily can be found as aromatic amino acids, secondary products abundantly generated by plants, structural components of the very complex lignin heteropolymer in woody plants, and xenobiotic compounds: biocides, industrial by-products, and petroleum derivatives, among others. Microorganisms may degrade hundreds of different AC using specialized biochemical pathways that allow them to grow on these carbon sources (1-3). Typically, bacteria deal with AC as part of complex mixtures in naturally occurring organic compounds, such as those found in plant exudates (4), in soils (5), and even in dissolved organic matter from freshwater and seawater (6). Therefore, microorganisms are concurrently exposed to several structurally heterogeneous AC as potential substrates, which raises the question of whether the components of these mixtures are used simultaneously or in a sequential manner. In the case of the sequential utilization pattern, characterized by diauxic growth, one compound inhibits degradation of the other by exerting metabolite toxicity (7), competitive inhibition of enzymes (8, 9), depletion of electron acceptors (10, 11),...