TABLE 5.
Syntrophic degradation of cyclohexane
| Microorganism(s) | Carbon source(s) | Extent of degradation for cyclohexane (%)a | Final amt (μmol) of:
|
||
|---|---|---|---|---|---|
| Cyclohexane | Cyclohexanone | Cyclohexene | |||
| A. lwoffii IFP 2149 | Cyclohexane | <5b | 23.0b | <0.1b | <0.1b |
| 2,2,4-Trimethylpentane + cyclohexane | <5b | 24.7b | <0.1b | <0.1b | |
| Mycobacterium sp. strain IFP 2173 | Cyclohexane | <5b | 23.4b | 1.2b | <0.1b |
| 2,2,4-Trimethylpentane + cyclohexane | 62 ± 4c | 9.2 ± 0.7c | 12.4 ± 0.8c | 1.2 ± 0.2c | |
| Mycobacterium sp. strain IFP 2173 + A. lwoffii IFP 2149 | Cyclohexane | <5b | 24.9b | <0.1b | <0.1b |
| 2,2,4-Trimethylpentane + cyclohexane | 65 ± 5c | 8.4 ± 0.9c | <0.1c | 1.2 ± 0.1c | |
The degradation rates were calculated as described in Materials and Methods. The amount of cyclohexane recovered in abiotic flasks was 23.9 ± 1.3 μmol.
The value is the mean based on the values obtained for two test flasks.
The values are the mean ± standard deviation based on the values obtained for three test flasks.