TABLE 4.
Quinones adsorbed to PM isolated from different sources (Mirivel et al., 2010)
| Particulate concentration (µg/g) |
||||||
|---|---|---|---|---|---|---|
| Quinone | Diesel particulate | Kerosene soot | Urban particulate reference material SRM 1648a | Indoor dust reference material SRM 2584 | Vehicle exhaust reference material NIES No. 8 | Urban dust reference material SRM 1649a |
| 9,10-Anthraquinone | 37.5 | 39.3 | 3.2 | 1.7 | 14.1 | 2.4 |
| 9,10-Phenanthroquinone | 26.1 | < 1.6 | 0.5 | < 0.1 | 11.4 | 1.1 |
| 2-Methyl-9,10-anthraquinone | 30.3 | < 4.5 | 1.4 | 0.5 | 4.1 | 1.0 |
| 1,2-Benzofluorenone | 4.8 | 11.7 | 2.5 | 0.9 | 1.5 | 2.0 |
| benzanthrone | 8.7 | 227.2 | 4.5 | 0.6 | 1.9 | 4.6 |
| 5,6-Chrysenequinone | < 10.4 | < 39.9 | < 2.5 | < 2.3 | < 1.5 | < 3.7 |
| 2-Fluorenecarboxaldehyde | < 6.3 | 1,128.1 | < 1.5 | < 1.4 | < 0.9 | < 2.3 |
| 1,2-Benzanthraquinone | < 4.0 | < 15.4 | 3.3 | 1.6) | < 0.6 | 3.4 |
| 5,12-Naphthacenequinone | < 29.3 | < 112.9 | < 7.0 | < 6.5 | < 4.2 | < 10.5 |
Bold type highlights those substances that are potentially useful biomarkers of diesel exhaust exposure.