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Environmental Health Criteria 214

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HUMAN EXPOSURE ASSESSMENT<br />

Few published data are available on the validity of the<br />

measurement of culturable fungi in settled dust as estimate of<br />

exposure. The results, both quantitatively and qualitatively, depend<br />

on the method of inoculation of the dust and on the culture medium<br />

used (Verhoeff et al., 1994a). The reproducibility of duplicate<br />

analyses in terms of CFU/g dust is acceptable, but in terms of species<br />

isolated only moderate. However, as is the case for air sampling, a<br />

single dust sample is a poor estimate of exposure to fungi over time<br />

(Verhoeff et al., 1994a).<br />

9.4.3 Available methods of analysis for fungi in air<br />

Air samples obtained with sampling devices collecting total<br />

fungal particles can be analysed by direct examination to obtain total<br />

counts of fungal particles. Samples collected on culture media have to<br />

be incubated to obtain counts of viable fungal particles. Dust can be<br />

plated either directly on to a culture medium or suspended and diluted<br />

prior to plating. Total counts of fungal particles in dust can also be<br />

obtained by partitioning into an aqueous two-phase system followed by<br />

epifluorescence microscopy (Strom et al., 1987).<br />

Samples are incubated for at least 4 days; up to 7 days is the<br />

typical time needed for spores to generate identifiable colonies. The<br />

temperature at which samples are incubated affects the recovery of<br />

culturable fungi. Since most environmental fungi grow well between<br />

20°C and 30°C, the incubation temperature is generally 25°C (EC,<br />

1993).<br />

Sporulating colonies are identified by colour and texture, by the<br />

naked eye or microscopically. Non-sporulating spores might be<br />

transferred to different agar and exposed to different lighting in an<br />

attempt to colonize them. Fungal genera are sometimes reported and<br />

provide important insight into sources and possible health effects.<br />

Common outdoor fungi are Cladosporium, Alternaria, Botrytis and<br />

Epicoccum. Penicillium, Aspergillus and Stachybotrys can be found<br />

in higher concentrations indoors. It is difficult to generalize and<br />

there is considerable variability over time so it is important to<br />

simultaneously collect outdoor samples. Fig. 28 shows the distribution<br />

of viable mould spores collected inside and outside homes in Australia<br />

(Garrett, 1996). Outdoor viable spore counts decrease in the winter<br />

and so do the indoor levels for homes without substantial sources of<br />

sporulating fungi.<br />

http://www.inchem.org/documents/ehc/ehc/ehc<strong>214</strong>.htm<br />

Page 162 of 284<br />

6/1/2007

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