Airborne fungal cell fragments in homes in relation to total fungal biomass

被引:23
作者
Adhikari, A. [1 ]
Reponen, T. [1 ]
Rylander, R. [2 ]
机构
[1] Univ Cincinnati, Dept Environm Hlth, Cincinnati, OH USA
[2] BioFact Environm Hlth Res Ctr, S-44391 Lerum, Sweden
关键词
Fungi; Endotoxin; beta-Glucan; Particle fractions; N-Acetylhexosaminidase; Air sampling; INDOOR AIR; MOLD; ASTHMA; DISEASE; COMPONENTS; ENDOTOXIN; DUST; PM1;
D O I
10.1111/j.1600-0668.2012.00799.x
中图分类号
TU [建筑科学];
学科分类号
0813 ;
摘要
Fungal exposure may induce respiratory symptoms. The causative agents are compounds in the fungal cell wall. Fragments of microbes may be present in air samples but are not measurable using conventional spore counting or by the determination of viable organisms. This study assesses the proportion of fungal cell biomass and endotoxin in different particle size fractions in air samples from homes. Air samples were collected from 15 homes using a cyclone sampler, collecting particles in three aerodynamic size fractions: <1.0, 1.01.8, and >1.8m. N-Acetylhexosaminidase (NAHA) was determined as a marker of fungal cell biomass. Endotoxin was determined using the Limulus amebocyte lysate method. NAHA and endotoxin in the size range <1.0m comprised up to 63% (mean 22.7%) and 96.3% (mean 22.6%) of the total concentrations, respectively. There were significant relationships between the amounts of NAHA and endotoxin in the total amount and in the size fraction >1.8m but not in the smaller fractions. The results demonstrate significant amounts of fungal cell biomass and endotoxin in particles <1.0m. Homes with reported mold damage had a lower concentration of NAHA in particles <1.0m than homes without mold damage. To assess airborne exposure for diagnostic and preventive purposes, measurement techniques that include this fraction should be considered.
引用
收藏
页码:142 / 147
页数:6
相关论文
共 32 条
[1]   Performance of the Button Personal Inhalable Sampler for the measurement of outdoor aeroallergens [J].
Adhikari, A ;
Martuzevicius, D ;
Reponen, T ;
Grinshpun, SA ;
Cho, SH ;
Sivasubramani, SK ;
Zhong, W ;
Levin, L ;
Kelley, AL ;
St Clair, HG ;
Lemastersa, G .
ATMOSPHERIC ENVIRONMENT, 2003, 37 (34) :4723-4733
[2]   The medical effects of mold exposure [J].
Bush, RK ;
Portnoy, JM ;
Saxon, A ;
Terr, AI ;
Wood, RA .
JOURNAL OF ALLERGY AND CLINICAL IMMUNOLOGY, 2006, 117 (02) :326-333
[3]   Aerodynamic characteristics and respiratory deposition of fungal fragments [J].
Cho, SH ;
Seo, SC ;
Schmechel, D ;
Grinshpun, SA ;
Reponen, T .
ATMOSPHERIC ENVIRONMENT, 2005, 39 (30) :5454-5465
[4]  
Delfino RJ, 1997, ENVIRON HEALTH PERSP, V105, P622, DOI 10.2307/3433608
[5]   Characterization of primary biogenic aerosol particles in urban, rural, and high-alpine air by DNA sequence and restriction fragment analysis of ribosomal RNA genes [J].
Despres, V. R. ;
Nowoisky, J. F. ;
Klose, M. ;
Conrad, R. ;
Andreae, M. O. ;
Poeschl, U. .
BIOGEOSCIENCES, 2007, 4 (06) :1127-1141
[6]   Measurement of beta(1->3)-glucans in occupational and home environments with an inhibition enzyme immunoassay [J].
Douwes, J ;
Doekes, G ;
Montijn, R ;
Heederik, D ;
Brunekreef, B .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1996, 62 (09) :3176-3182
[7]  
Fajt Merritt L, 2009, Expert Rev Respir Med, V3, P607, DOI 10.1586/ers.09.57
[8]   Meta-analyses of the associations of respiratory health effects with dampness and mold in homes [J].
Fisk, W. J. ;
Lei-Gomez, Q. ;
Mendell, M. J. .
INDOOR AIR, 2007, 17 (04) :284-296
[9]   Fungal fragments as indoor air biocontaminants [J].
Górny, RL ;
Reponen, T ;
Willeke, K ;
Schmechel, D ;
Robine, E ;
Boissier, M ;
Grinshpun, SA .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 2002, 68 (07) :3522-3531
[10]   Culturable mold in indoor air and its association with moisture-related problems and asthma and allergy among Swedish children [J].
Holme, J. ;
Hagerhed-Engman, L. ;
Mattsson, J. ;
Sundell, J. ;
Bornehag, C. -G. .
INDOOR AIR, 2010, 20 (04) :329-340