Pseudomonas acidovorans and Pseudomonas sp. strain ANL but not Salmonella typhimurium grew in an inorganic salts solution. The growth of P. acidovorans in this solution was not enhanced by the addition of 2.0 jig of phenol per liter, but the phenol was mineralized. Mineralization of 2.0 jig of phenol per liter by P. acidovorans was delayed 16 h by 70 ,ug of acetate per liter, and the delay was lengthened by increasing acetate concentrations, whereas phenol and acetate were utilized simultaneously at concentrations of 2.0 and 13 jig/liter, respectively. Growth of Pseudomonas sp. in the inorganic salts solution was not affected by the addition of 3.0 jig each of glucose and aniline per liter, nor was mineralization of the two compounds detected during the initial period of growth. However, mineralization of both substrates by this organism occurred simultaneously during the latter phases of growth and after growth had ended at the expense of the uncharacterized dissolved organic compounds in the salts solution. In contrast, when Pseudomonas sp. was grown in the salts solution supplemented with 300 jig each of glucose and aniline, the sugar was mineralized first, and aniline was mineralized only after much of the glucose carbon was converted to CO2. S. typhimurium failed to multiply in the salts solution with 1.0 jig of glucose per liter. It grew slightly but mineralized little of the sugar at 5.0 jig/liter, but its population density rose at 10 jig of glucose per liter or higher. The hexose could be mineralized at 0.5 jig/liter, however, if the solution contained 5.0 mg of arabinose per liter. In solutions with this arabinose concentration and glucose levels too low to support growth, the percentage of glucose carbon incorporated into S. typhimurium cells was the same as when the bacterium was grown in solutions with high concentrations of glucose alone. When glucose was the only carbon source for S. typhimurium, the percentage of the glucose carbon assimilated and mineralized progressively declined as the sugar concentration was reduced to levels approaching the threshold for growth. These results indicate that second substrates and uncharacterized dissolved organic carbon may play an important role in controlling the rate and extent of biodegradation of organic compounds at low concentrations. Microorganisms can degrade a variety of synthetic organic compounds present in samples from natural environments at concentrations below 10 puglliter (1, 16). However, it is not certain whether microorganisms can grow at such low concentrations. It has been postulated that substrate uptake will just meet maintenance energy requirements and growth is not possible at sufficiently low substrate concentrations (12). * Corresponding author. to use the uncharacterized DOC were used. In addition, to understand the effect of DOC on the metabolism of synthetic organic substrates, studies were also conducted on the effects of second substrates on the biodegradation of low concentrations of organic compounds. MATERIALS AND METHODS Rad...