The contribution of fungi on
bioaerosol emissions was not investigated in this study because
the fungal emission in solid-waste composting has been previously
reported to be of less significance (Nikaeen et al., 2009; Taha et al.,
2005). Emission profiles are shown in Fig. 2. Data were analyzed
using a dynamic calibration method and data fitting was performed
using Sigmaplot (Version 10.0, Systat Software, Inc., USA). Correlation
coefficient (R2) for all parameters were over 0.97. The peak of
the airborne culturable bacteria emissions coincided with the thermophilic
stage. The concentration of airborne bacteria increased to
31,250 CFU/m3 and then decreased to below the detection limit.
Because the composting process proceeds quickly, the quantification
of bioaerosol and its variation could be underestimated
The contribution of fungi on
bioaerosol emissions was not investigated in this study because
the fungal emission in solid-waste composting has been previously
reported to be of less significance (Nikaeen et al., 2009; Taha et al.,
2005). Emission profiles are shown in Fig. 2. Data were analyzed
using a dynamic calibration method and data fitting was performed
using Sigmaplot (Version 10.0, Systat Software, Inc., USA). Correlation
coefficient (R2) for all parameters were over 0.97. The peak of
the airborne culturable bacteria emissions coincided with the thermophilic
stage. The concentration of airborne bacteria increased to
31,250 CFU/m3 and then decreased to below the detection limit.
Because the composting process proceeds quickly, the quantification
of bioaerosol and its variation could be underestimated
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