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`tµ•Mrc 5 so;i colony forming units per swab because the actual raw counts have to be multiplied by the dilutions used, in this case 10,000 dilution. While this technique is generally used in microbiology (generally bacteria counts due to their exponential growth and extremely high numbers), one has to be very cautious interpreting the results. To a non-technical person,these huge numbers may cause fear that individuals may be exposed to extremely high levels when in reality that is not the case. The presence of mold on surfaces or the results of surface samples cannot be used to estimate air mold spores or estimate exposure via inhalation. Air sampling methods are used to estimate the airborne concentrations of mold spores and mold particles, that is,the relevant exposure pathway in humans to indoor mold is inhalation. The analyses of the spore trap air samples collected by AMEC in July 2014 and March/April 2015, analyzed by EMSL Analytical, Inc. and EMLab P&K,respectively(AMEC, Reports of Limited Inspections and Indoor Air Quality Assessment,Indian River County Fire Stations 1, 7, 10, and 11,reports dated September 10 and18,2014, with EMSL Analytical,Inc.test reports),clearly indicates that very little spores were aerosolized in the air when compared to the outdoor data. It is noteworthy to mention that the growth of actual mold, such as those reported here(e.g. Stachybotrys, Cladosporium,or Penicillium)on surfaces (EMLab P&K,Direct Microscopic Examination Reports, dated April 6, 2015), does not correlate with the amount of mold spores in the air. None of these molds forcibly discharges their spores into the air. They require wind or some mechanical disturbance to dislodge their spores and then may become airborne. In the case of Stachybotrys mold,the chances of spores becoming airborne are even much less, as this mold forms sticky masses of spores and are not air dispersed and may be insect or rain splash dispersed. 74