TABLE 1.
Background Values (μ g/m3)a
obs | mean | median | SD | |
---|---|---|---|---|
trimethylpentane | 432 | 0.71 | 0.43 | 0.79 |
dimethylpentane | 432 | 0.38 | 0.24 | 0.47 |
2-methylhexane | 432 | 0.64 | 0.42 | 0.95 |
methylpentane | 432 | 1.60 | 1.04 | 2.28 |
3-methylhexane | 432 | 0.76 | 0.48 | 1.28 |
methylcyclohexane | 432 | 0.46 | 0.27 | 0.68 |
hexane | 161 | 1.70 | 1.01 | 1.86 |
1,3-butadiene | 432 | 0.20 | 0.12 | 0.45 |
benzene | 432 | 1.24 | 1.01 | 0.87 |
ethylbenzene | 432 | 0.56 | 0.40 | 0.53 |
m,p-xylene | 432 | 1.85 | 1.36 | 1.69 |
o-xylene | 432 | 0.66 | 0.46 | 0.63 |
styrene | 432 | 0.26 | 0.15 | 0.36 |
toluene | 432 | 3.67 | 2.77 | 3.43 |
toluene/benzene | 432 | 3.0 | 2.7 | n/a |
MTBE | 432 | 0.27 | 0.01 | 0.53 |
acetone | 345 | 2.62 | 1.75 | 3.07 |
acetaldehyde | 345 | 2.42 | 2.06 | 2.45 |
formaldehyde | 345 | 3.33 | 3.22 | 1.75 |
elemental carbon | 432 | 0.83 | 0.57 | 0.77 |
PM2.5 | 427 | 11.67 | 9.30 | 14.63 |
The differences across locations (yard background, driver, loading dock, and mechanic shop) for all concentrations were statistically significant (p < 0.01) using Kruskal–Wallis nonparametric comparison tests.