Table 4.
Localization | Determined compounds | Sampling technique | Applied sorption medium | Technique for the separation/liberation of analytes | Final determination technique | Average concentration | Ref. |
---|---|---|---|---|---|---|---|
2 residential basementsa, Massena and Lisbon, NY, USA | Methanol | Dynamic (400-mL, 1-L, and 6-L evacuated stainless steel canisters) | Lack of applied sorption medium | Lack of applied analyte liberation technique—direct injection of gas sample | GC-FID | 5839 ± 3800 ppb | Soto-Garcia et al. (2015) |
Pentane | 100 ± 61 ppb | ||||||
Pentanal | 86 ± 53 ppb | ||||||
Hexanal | 214 ± 176 ppb | ||||||
74 residences, Detroit, MI, USA | VOCs | Passive | Not mentioned | Thermal desorption | GC-MS | Benzene: 5.88 μg/m3, toluene: 77.30 μg/m3, naphthalene: 65.78 μg/m3, limonene: 21.95 μg/m3 | Du et al. (2015) |
55 residences, Boston, MA, USA | Formaldehyde | Dynamic | 2,4-Dinitro-phenylhydrazine-coated silica cartridges (Waters Corp.) | Ozone scrubbers containing potassium iodide | HPLC-UV(operating at 360 nm) | 12 μg/m3 | Dodson et al. (2008) |
Acetaldehyde | 8.5 μg/m3 | ||||||
Other VOCs | Dynamic | Triple-bed tube with Carbopach B, Carbopack X, and Carboxen | Thermal desorption | GC-MS | Methylene chloride: 9.5 μg/m3, chloroform: 0.57 μg/m3, trichloroethene: 0.43 μg/m3, tetrachloroethene: 1.7 μg/m3, 1,4-dichlorobenzene: 1.3 μg/m3, 1,3-butadiene: 0.5 μg/m3, MTBE: 8.8 μg/m3, benzene: 3.2 μg/m3, toluene: 21 μg/m3, ethylbenzene: 4.1 μg/m3, m,p-xylene: 12 μg/m3, o-xylene: 4.2 μg/m3, styrene: 1.7 μg/m3, α-pinene: 11 μg/m3, d-limonene: 8.8 μg/m3 |
aBasements dedicated to store large fabric bags with blended mixture pellets