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. 1998 Aug;64(8):2914–2919. doi: 10.1128/aem.64.8.2914-2919.1998

TABLE 4.

Weekly geometric mean emissions of VOCs during 10 to 12 weeks of incubation of contaminated building materials at three or four different RH levels and corresponding emissions from sterile building materials, as determined by GC-MS and HPLC

VOCa Weekly geometric mean yield (ng/liter)
Gypsum board, wallpaper, and plastic film
Chipboard and glass wool
Ceramic tile
Contaminated (n = 12) Sterile (n = 12) Pb Contaminated (n = 12) Sterile (n = 12) Pb Contaminated (n = 10) Sterile (n = 10) Pb
3-Methyl-1-butanol ND–3c ND ND–35 ND ND–10 ND–8
1-Hexanol ND–24 ND–9 ND–470 ND–8 ND–78 ND ∗∗
Limonene 10–44 7–44 ∗∗ 54–550 54–940 8–41 7–65
Acetone 18–520 19–490 ND–8,100 190–9,100 17–290 ND–300
Butanone ND–500 ND–160 ND–940 ND–920 ND–310 ND–230 ∗∗
2-Pentanone ND–30 ND–110 ND–1,700 ND–530 ND–220 ND–160
3-Methyl-2-pentanone ND–50 ND–49 ND–300 ND–370 ND–95 ND–71
2-Hexanone ND–31 ND–280 ND–460 ND–620 ND–290 ND–99
3-Octanone ND–15 ND–22 ND–40 ND–27 ND–17 ND–14
a

Only those VOCs regarded as MVOCs with at least one building material are included. 

b

Statistical significance as determined by the Wilcoxon test. †, the yield from the contaminated construction material was not statistically significantly higher than the yield from the sterile construction material; ∗, 0.01 ≤ P ≤ 0.05; ∗∗, P < 0.01. 

c

ND, not detected.