Applicability of a modified MCE filter method with Button Inhalable Sampler for monitoring personal bioaerosol inhalation exposure.
In this study, a "modified" mixed cellulose ester (MCE) filter culturing method (directly placing filter on agar plate for culturing without extraction) was investigated in enumerating airborne culturable bacterial and fungal aerosol concentration and diversity both in different environments. A Button Inhalable Sampler loaded with a MCE filter was operated at a flow rate of 5 L/min to collect indoor and outdoor air samples using different sampling times: 10, 20, and 30 min in three different time periods of the day. As a comparison, a BioStage impactor, regarded as the gold standard, was operated in parallel at a flow rate of 28.3 L/min for all tests. The air samples collected by the Button Inhalable Sampler were directly placed on agar plates for culturing, and those collected by the BioStage impactor were incubated directly at 26 °C. The colony forming units (CFUs) were manually counted and the culturable concentrations were calculated both for bacterial and fungal aerosols. The bacterial CFUs developed were further washed off and subjected to polymerase chain reaction-denaturing gradient gel electrophoresis (DGGE) for diversity analysis. For fungal CFUs, microscopy method was applied to studying the culturable fungal diversity obtained using different methods. Experimental results showed that the performance of two investigated methods varied with sampling environments and microbial types (culturable bacterial and fungal aerosols). For bacterial aerosol sampling, both methods were shown to perform equally well, and in contrast the "modified" MCE filter method was demonstrated to enumerate more culturable fungal aerosols than the BioStage impactor. In general, the microbial species richness (number of gel bands) was observed to increase with increasing collection time. For both methods, the DGGE gel patterns were observed to vary with sampling time and environment despite of similar number of gel bands. In addition, an increase in sampling time from 20 to 30 min was found not to substantially alter the species richness. Regardless of the sampling methods, more species richness was observed in the outdoor environment than the indoor environment. This study described a new personal bioaerosol exposure assessment protocol, and it was demonstrated applicable in monitoring the personal bioaerosol exposure in replace of an Andersen-type impactor.
State Key Joint Laboratory for Environmental Simulation and Pollution Control College of Environmental Sciences and Engineering, Peking University, Beijing 100871, China.
Zhenqiang
Z
Xu
Hong
H
Xu
Maosheng
M
Yao
D000336:Aerosols / Q000032:analysis*; D000391:Air Microbiology; D000393:Air Pollutants / Q000032:analysis*; D001419:Bacteria / Q000145:classification / Q000302:isolation & purification*; D044822:Biodiversity; D002482:Cellulose / Q000378:metabolism; D015169:Colony Count, Microbial; D058645:Denaturing Gradient Gel Electrophoresis; D004784:Environmental Monitoring / Q000295:instrumentation / Q000379:methods*; D004952:Esters / Q000378:metabolism; D005374:Filtration / Q000379:methods; D005658:Fungi / Q000145:classification / Q000302:isolation & purification*; D019570:Inhalation Exposure / Q000032:analysis*; D016133:Polymerase Chain Reaction; D013048:Specimen Handling / Q000295:instrumentation / Q000379:methods; D013997:Time Factors
D000336:Aerosols; D000393:Air Pollutants; D004952:Esters; D002482:Cellulose