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from: Health & Environment Digest Vol 10, No. 2,
pages 9-12, May/June 1996
Fungi & Indoor Air Quality
Sandra V. McNeel, DVM
Richard A. Kreutzer, MD
California Department of Health Services
Environmental Health Investigations Branch
Introduction
While occupational exposure to airborne pollutants such as
asbestos and coal dust is known to cause lung cancer/mesothelioma
and pneumoconiosis (black lung disease), consequences of exposure to
air contaminants, especially bioaerosols, in homes and
non-industrial work sites such as office buildings are not yet fully
understood. In the 1970's and 1980's microbial contamination was
identified as the primary cause for poor air quality in only 5% of
more than 500 indoor air quality (IAQ) investigations conducted by
National Institute for Occupational Safety and Health (NIOSH); while
the remaining 95% resulted from inadequate ventilation, entrainment
of outdoor air contaminants, contaminants in building fabric and
unknown sources (NIOSH, 1989). However, in the last 10 years,
microorganisms were the primary source of indoor air contamination
in as many as 35-50% of IAQ cases (Lewis, 1994). This change has
been attributed at least partially to a paradigm shift from chemical
contaminant-based investigations to an interdisciplinary approach
combining evaluation of physical, chemical and microbiological
constituents of indoor air environments. This report specifically
focuses on fungal contamination in office and home environments.
Molds in Indoor Air
Fungi are ubiquitous organisms that make up approximately 25% of
earth's biomass. They can be subdivided somewhat artificially by
gross morphology into yeasts, mushrooms and molds - the fungi
of most importance for indoor air. Molds are very adaptable and can
colonize dead and decaying organic matter (e.g. textiles, leather,
wood, paper) and even damp, inorganic material (e.g. glass, painted
surfaces, bare concrete) if organic nutrients such as dust or soil
particles are available. Because various genera grow and reproduce
at different substrate water concentrations and temperatures, molds
occur in a wide range of habitats.
Constituents of indoor air are determined by both outdoor and
indoor sources (Table 1). Likewise mold types and concentrations
indoors are primarily a function of outdoor fungi and substrate
water (related to indoor humidity level). Higher concentrations of
outdoor molds and other fungi occur where trees, shrubs and
landscape irrigation occur close to exterior building walls. (While
most indoor molds originate from exterior sources, some species of
Aspergillus and Penicillium can grow and reproduce
effectively indoors and are commonly found in air samples of normal,
"dry" buildings.)
Molds are composed of linear chains of cells (hyphae) that branch
and intertwine to form the fungus body (mycelium). All fungal cell
walls contain (1-3)-beta-D-glucan, a medically significant glucose
polymer that has immunosuppressive, mitogenic (i.e. causing mitosis
or cell transformation) and inflammatory properties. This mold cell
wall component also appears to act synergistically with bacterial
endotoxins to produce airway inflammation following inhalation
exposure in guinea pigs (Fogelmark et al., 1994).
Under certain metabolic conditions, many fungi produce mycotoxins,
natural organic compounds that initiate a toxic response in
vertebrates. While some mycotoxins have been found to be associated
with hyphae, the primary mode of human exposure to mycotoxins and is
inhalation of spores and mold-contaminated material. Molds that are
important potential producers of toxins indoors are certain species
of Fusarium, Penicillium, and Aspergillus. In
water-damaged buildings Stachybotrys chartarum (a.k.a.
atra) and Aspergillus versicolor may also produce
toxic metabolites. A large body of information is available on the
human and animal health effects from ingestion of certain mycotoxins
(Beasley, 1994; Sorenson, 1989; Smith and Henderson,1991), but
investigators have only recently begun to explore the health
implications of inhalation exposure to these substances. Two classes
of mycotoxins have been isolated from house dust samples: aflatoxins
from some strains of Aspergillus flavus and trichothecenes
from some species and strains of Fusarium, Cephalosporium,
Stachybotrys and Trichoderma. In laboratory animals,
inhalation of trichothecene mycotoxins causes severe inhibition of
protein synthesis and immunosuppression (Beasley, 1994). Several
case reports have associated overgrowths of trichothecene-producing
fungi with human health effects such as cold and flu-like symptoms,
sore throats, headache and general malaise (Croft et al., 1986;
Johanning et al., 1993; Nikulin et al., 1994). However, isolation of
a toxigenic fungus from a building does not imply the presence of
mycotoxin, since the physical conditions necessary for mycotoxin
production are very specific, and are often different from those
required for growth of the parent mold. Likewise, failure to produce
toxins in vitro does not mean that a mold known to be
toxogenic will not produce toxins in a field situation.
Molds also produce a large number of volatile organic compounds (VOCs).
These chemicals are responsible for the musty odors produced by
growing molds. There is little evidence that fungal VOCs cause
specific human health effects (Batterman, 1995), but the most common
VOC, ethanol, is a potent synergizer of many fungal toxins.
Health effects associated with molds
Molds produce acute health effects through toxin-induced
inflammation, allergy, or infection. There is no information at this
time on the effects of chronic, low dose inhalation exposure to
mycotoxins.
Toxin-induced inflammation: Repeated or high exposures to
airborne mycotoxins can cause mucous membrane irritation
characterized by eye, nose and throat irritation (Richerson, 1990).
When small diameter spores (2-4 µm) are inhaled, they may reach the
lung alveoli and induce an inflammatory reaction, creating toxic
pneumonitis. Severe toxic pneumonitis can cause fever, flu-like
symptoms and fatigue (organic toxic dust syndrome). Hypersensitivity
pneumonitis, a particular form of granulomatous lung disease, is a
syndrome caused by inhalation of large concentrations of dust
containing organic material including fungal spores. It is generally
an occupational hazard in agriculture, but has been reported in
individuals exposed in the home (Flannigan, et al., 1991).
Other symptoms attributed to mycotoxin or fungal-origin VOCs include
headache, dizziness, dermatitis, diarrhea and impaired or altered
immune function.
Allergy: Indoor fungal allergens probably affect fewer people
than do allergens from cats, mites or cockroaches. Yet a significant
proportion (10-32%) of all asthmatics are sensitive to fungi. More
thorough discussion of fungal allergens is available elsewhere
(Horner, et al. 1995; Einarsson, et al. 1992; Burge, 1985).
Infection: Opportunistic fungal pathogens such as
Aspergillus are common in indoor air. A normal, healthy
individual can probably resist infection by these organisms
regardless of dose, although high exposures may cause
hypersensitivity pneumonitis. However, any mold that can grow at
body temperature can become a pathogen in an immuno-compromised
host. Individuals undergoing chemotherapy, organ or bone marrow
transplantation or those with HIV/AIDS are especially susceptible to
invasive infection by Aspergillus species.
Some examples of indoor molds, their products and possible health
effects are given in Table 2.
Prevention and Control
Although we don’t fully understand how or when indoor fungi
affect human health, we do have enough evidence to recommend
controlling these organisms in indoor environments. Since fungal
spores and conidia are ubiquitous, the most effective method of
source control is elimination of moisture that supports mold growth.
This may involve fixing leaking pipes, windows or roofs, directing
rainfall or irrigation drainage away from exterior walls, or
increasing insulation. Using fans or opening windows may also be
helpful. Ventilation systems, especially those in large commercial
buildings, should be properly maintained and examined periodically
for microbial contamination.
When underlying moisture sources cannot be readily eliminated,
air conditioners and dehumidifiers can help control relative
humidity. When using dehumidifiers, water collection traps should be
cleaned routinely as these are another source of microbial growth.
Visible mold can be removed by disinfection with a chlorine bleach
solution. The area being cleaned should be well-ventilated, as
chlorine itself is volatile and irritating.
Directions of Future Research
There are many gaps in our knowledge of human health effects
associated with inhalation exposure to indoor molds. Important
research topics include:
w defining how fungal toxins impair
immune systems,
w quantifying relationship of dose
and duration of exposure to airborne mycotoxins,
w developing efficient methods to
identify and analyze mycotoxins in the field,
w determining effects of
varying environmental conditions (substrate temperature,
relative humidity, material moisture content) on mycotoxin
production, and
w examining potential human
health effects from exposure to combinations of indoor
contaminants such as environmental tobacco smoke, VOCs, carbon
monoxide, mycotoxins and other microbial components.
Acknowledgment: The authors thank Dr. Janet Macher,
California Department of Health Services, Environmental Health
Lab, for her thoughtful review of this document.
TABLE 1
Selected Important Molds Found in Damp Buildings
| Fungal Species |
Substrate |
Possible Metabolites |
Potential Health Effects* |
| Alternaria
alternata |
moist window-sills, walls |
allergens |
asthma, allergy |
| |
|
|
|
| Aspergillus
versicolor |
damp wood, wallpaper glue |
mycotoxins,
VOCs |
unknown |
| |
|
|
|
| Aspergillus
fumigatus |
house dust, potting soil |
allergens
|
asthma, rhinitis, hypersensitivity pneumonitis
|
| |
|
many mycotoxins |
toxic pneumonitis
infection** |
| |
|
|
|
| Cladosporium
herbarum |
moist window-sills, wood |
allergens |
asthma, allergy |
| |
|
|
|
| Penicillium
chrysogenum |
damp wallpaper, behind paint |
mycotoxins
|
unknown |
| |
|
VOCs |
unknown |
| |
|
|
|
| Penicillium
expansum |
damp wallpaper |
mycotoxins |
nephrotoxicity? |
| |
|
|
|
| Stachybotrys
chartarum (atra) |
heavily wetted carpet,
gypsum board |
mycotoxins |
dermatitis, mucosal irritation,
immunosuppression |
| |
|
|
|
* specifically from inhalation exposure, based on laboratory
animal data
** in immuno-compromised individuals
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