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. 2021 Feb 15;65(4):446–457. doi: 10.1093/annweh/wxaa129

Table 2.

Concentrations of air contaminants determined by stationary sampling during paving with hot mix asphalt (HMA) and warm mix asphalt (WMA).

HMA WMA P-value (95 % CId) GSD for the difference between HMA and WMA Variance component within sampling positions Variance component between sampling positions
N  a GMb GSDc Min–max N GM GSD Min–max
Organic carbon (mg m−3) 30 0.18 2.30 0.06–1.27 30 0.09 2.32 0.01–0.32 <0.01 (0.47–0.94) 1.86 0.44 0.39
Asphalt vapor (p.p.m.) 27 0.08 4.03 0.004–0.44 27 0.04 5.57 0.001–0.52 0.02 (0.12–1.26) 4.20 1.60 0.89
Respirable fraction of PMe (mg m−3) 15 0.22 2.43 0.05–1.12 15 0.12 2.83 <0.03f–0.36 0.04 (0.04–1.28) 3.06 1.03 0.08
Thoracic fraction of PM (mg m−3) 15 0.24 2.26 0.05- 1.06 15 0.17 2.04 0.06–0.37 0.16 (−0.16–0.88 2.56 0.71 0.03
Inhalable fraction of PM (mg m−3) 15 0.27 2.27 0.07– 1.21 15 0.23 1.89 0.06–0.44 0.4 (−0.27–0.65) 2.31 0.45 0.12

In each experiment, three parallel samples of each contaminant were collected. The statistical significance of differences in geometric means (GMs) was tested by performing a paired t-test on ln-transformed data. The variance between and within sampling positions were calculated using variance component analysis.

aNumber of measurements.

bGeometric mean.

c Geometric standard deviation.

dConfidence interval.

eParticulate matter.

fOne measurement was below the LOD.