Table 2.
Compound | Overall
|
By season
|
By day-of-the-week
|
||||||
---|---|---|---|---|---|---|---|---|---|
Nb | Geomean | 95th% | Summer | Winter | p-valuec | Weekday | Weekend | p-valued | |
WFS | |||||||||
MTBE | 200 | 2.24 ± 3.21 | 12.9 | 2.46 ± 3.28 | 2.03 ± 3.13 | 0.71 | 1.97 ± 3.26 | 2.61 ± 3.12 | 0.49 |
Benzene | 187 | 2.24 ± 2.05 | 7.24 | 2.20 ±2.16 | 2.28 ± 1.96 | 0.64 | 2.34 ±2.12 | 2.12 ± 1.98 | 0.41 |
Hexane | 181 | 3.46 ± 6.25 | 230 | 6.59 ± 10.1 | 1.95 ± 2.64 | <0.01 | 2.28 ± 2.68 | 5.26 ± 10.3 | 0.04 |
Toluene | 200 | 5.61 ± 2.56 | 17.4 | 5.48 ± 2.36 | 5.75 ± 2.78 | 0.42 | 6.26 ± 2.96 | 4.94 ± 2.05 | 0.09 |
Ethylbenzene | 200 | 0.88 ± 2.24 | 3.16 | 0.82 ± 2.36 | 0.95 ± 2.11 | 0.26 | 1.00 ± 2.27 | 0.76 ± 2.17 | 0.03 |
m/p-xylene | 200 | 2.58 ± 2.17 | 9.36 | 2.50 ±2.13 | 2.68 ± 2.22 | 0.45 | 2.90 ± 2.30 | 2.26 ± 1.98 | 0.04 |
o-xylene | 200 | 0.83 ± 2.12 | 2.66 | 0.82 ± 2.09 | 0.83 ± 2.16 | 0.05 | 0.92 ± 2.21 | 0.73 ± 1.97 | 0.05 |
Styrenee | 200 | 0.20 ± 2.25 | 0.78 | 0.14 ± 2.00 | 0.29 ± 2.13 | N/A | 0.22 ± 2.29 | 0.18 ± 2.18 | N/A |
Chloroform | 173 | 0.55 ± 2.67 | 3.32 | 0.68 ± 2.53 | 0.46 ± 2.72 | 0.05 | 0.57 ± 2.79 | 0.54 ± 2.57 | 0.60 |
Carbon tetrachloride | 173 | 0.50 ± 1.29 | 0.71 | 0.55 ± 1.24 | 0.45 ± 1.28 | <0.01 | 0.49 ± 1.30 | 0.50 ± 1.28 | 0.84 |
CDS | |||||||||
MTBE | 165 | 2.53 ± 2.96 | 17.9 | 2.71 ± 3.84 | 2.34 ± 2.02 | 0.62 | 2.54 ± 2.93 | 2.51 ± 3.01 | 0.45 |
Benzene | 153 | 3.10 ± 2.23 | 11.5 | 4.30 ± 2.29 | 2.28 ± 1.91 | <0.01 | 3.17 ± 2.19 | 3.03 ± 2.29 | 0.74 |
Hexane | 139 | 4.88 ± 7.53 | 1184 | 12.8 ± 13.9 | 2.34 ± 2.32 | <0.01 | 2.86 ± 2.43 | 8.27 ± 13.6 | 0.06 |
Toluene | 165 | 5.75 ± 2.69 | 24.4 | 5.47 ± 2.90 | 6.07 ± 2.47 | 0.74 | 6.09 ± 2.58 | 5.42 ± 2.81 | 0.75 |
Ethylbenzene | 165 | 0.98 ± 2.66 | 5.43 | 0.91 ± 2.71 | 1.05 ± 2.60 | 0.22 | 1.07 ± 2.30 | 0.89 ± 3.02 | 0.37 |
m/p-xylene | 165 | 2.67 ± 2.86 | 14.9 | 2.52 ± 2.91 | 2.84 ± 2.81 | 0.30 | 2.94 ± 2.48 | 2.41 ± 3.25 | 0.38 |
o-xylene | 165 | 0.87 ± 2.72 | 4.92 | 0.86 ± 2.79 | 0.88 ± 2.66 | 0.36 | 0.95 ± 2.49 | 0.80 ± 2.95 | 0.36 |
Styrenee | 165 | 0.21 ± 2.81 | 1.03 | 0.14 ± 2.95 | 0.32 ± 2.20 | N/A | 0.22 ± 2.62 | 0.19 ± 3.00 | N/A |
Chloroform | 130 | 0.65 ±4.18 | 6.95 | 0.86 ± 3.75 | 0.54 ± 4.37 | 0.04 | 0.67 ±4.10 | 0.63 ± 4.30 | 0.75 |
Carbon tetrachloride | 130 | 0.45 ± 1.35 | 0.66 | 0.49 ± 1.45 | 0.42 ± 1.25 | 0.02 | 0.46 ± 1.30 | 0.44 ± 1.40 | 0.38 |
Data are presented in geometric mean ± geometric standard deviation.
Total sample size: There were a few extremely high concentrations of benzene and hexane which may be due to solvent contamination, and were not included in calculation the distribution. Measurements of chloroform and carbon tetrachloride were added in the middle of the study, and thus have smaller sample size.
Comparison between the arithmetic mean summer and winter concentrations, p-value of t-test based on log-transformed concentrations.
Comparison between the arithmetic mean weekday and weekend concentrations, p-value of t-test based on log-transformed concentrations.
Comparisons by season and by day-of-the-week were not conducted on styrene concentrations, as only 32% of the styrene concentrations were above detection limit.