from: "California Morbidity", a monthly
report from Prevention Services,
California Department of Health
Services, April 1998
Health Effects of
Toxin-Producing Indoor Molds in
California
CA Department of Health Services
Environmental Health Investigations
Branch
Due to excessive rainfall this winter
many Californians are experiencing increased exposure to
indoor microorganisms. Several fungal species capable of
producing toxic substances have been found in
water-damaged California homes and offices. This article
provides information about potential health effects from
exposure to Stachybotrys chartarum (a.k.a. S.
atra), a toxigenic mold that has received increasing
attention recently among indoor air reseachers and the
public. Within the last 12-18 months several scientific
reports (and media attention) have focused on
Stachybotrys, a ubiquitous saprophytic fungus
that grows on nitrogen-poor, cellulose rich materials
such as hay, straw and building materials (ceiling
tiles, wall paper, paper covering on gypsum wallboard).
The statewide prevalence of this fungus in homes or work
places is unknown, although one report found
Stachybotrys in 2-3% of a small survey of southern
California homes (Kozak, 1979).
Mechanism of Action
Some strains of Stachybotrys
chartarum can produce mycotoxins of the
trichothecene and spirolactone families. The
trichothecene mycotoxins satratoxins G and H are potent
protein synthesis inhibitors and cause immunosuppression
in laboratory animals. In experimental animal studies,
the trichothecenes affect rapidly proliferating tissues
such as skin and mucosa, as well as lymphatic and
hematopoietic tissues (Ueno, 1983). In laboratory
animals, acute exposure to large amounts of
trichothecene toxins results in a rapid release of
sequestered white blood cells into circulation, while
repeated or chronic exposure destroys granulocytic
precursor cells in bone marrow leading to white cell
depletion. Among the reported cellular effects are:
mitogen B/T lymphocyte blastogenesis suppression;
decrease of IgM, IgG, IgA; impaired macrophage activity
and migration-chemotaxis; broad immunosuppressive
effects on the cellular and humoral-mediated immune
response leading to secondary infections; and,
paradoxically, increased spontaneous antibody producing
cells in the spleen (Corrier, 1991).
Toxigenic strains of SC may also
produce spirolactones (stachybotrylactone) and
spirolactams (stachybotrylactam), toxins which produce
anticomplement effects (Jarvis, 1995). Possible
synergistic effects between the trichothecenes and these
mycotoxins have not yet been evaluated. Although
laboratories can test a sample of Stachybotrys
chartarum for its ability to produce mycotoxins,
in vitro results do not necessarily equate with
the in vivo situation. Therefore, a fungus that
produces toxins in the lab may not do so in the field,
or vice versa. It has been suggested that to assure the
safety of any exposed individual, whenever
Stachybotrys chartarum is identified, it should
be considered as a potential mycotoxin-producing
organism (Jarvis, 1994).
Positive skin reactions to the fungus
have been found in some asthmatics living or working in
Stachybotrys-contaminated rooms, suggesting a
hypersensitivity component in addition to the potential
for mycotoxicosis. Thus the fungal spores themselves or
chemicals carried on the spores may produce either
allergenic or toxigenic effects (Flannigan,
1991).
Routes of Exposure
Due to its wet, slimy growth
characteristics, it is unusual for spores from active
Stachybotrys colonies to become aerosolized.
However, when colonies of this fungus die and become
dehydrated, there is increased risk for air dispersion.
Portals of possible entry into the body include
inhalation and dermal absorption when the fungus is
found on walls or in carpets.
Case Reports
Historically, toxicologic effects from
this fungus were reported in Europe, where horses, sheep
and cattle suffered fatal hemorrhagic disorders
following ingestion exposures (Forgacs,1972)). Human
occupational exposures to contaminated straw or hay
resulted in nasal and tracheal bleeding, skin irritation
and alterations in white blood cell counts (Hintikka,
1987).
The first U.S. case of
Stachybotrys-associated health effects from inhalation
exposure was reported in a suburban Chicago family
(Croft, 1986). The fungus had contaminated the
ventilation system and ceilings of the house. Health
effects reported by the family included chronic
recurring cold and flu-like symptoms, sore throat,
diarrhea, headache, fatigue, dermatitis, intermittent
focal alopecia and generalized malaise. Workers who
cleaned and removed contaminated material from this
house also experienced skin irritation and respiratory
symptoms. After Stachybotrys contamination was
removed the house was reoccupied and residents reported
no recurrence of clinical symptoms.
Stachybotrys and satratoxin H (one
of the trichothecene mycotoxins) were subsequently
identified in a water-damaged office building in New
York City. A small case-control study showed workers
exposed to the fungus were at statistically significant
higher risk for nonspecified disorders of the lower
airways, eyes and skin; fevers and flu-like symptoms,
and chronic fatigue (Johanning, 1993, 1996). No
significant differences in specific S. chartarum
IgE and IgG levels were noted between cases and
controls. Although Stachybotrys chartarum
specific IgE (RAST) and IgG (ELISA) tests are available,
their sensitivity and specificity have not yet been
determined.
A recent report describes
identification of 10 likely or possible cases of
building-related asthma in a courthouse contaminated
with Stachybotrys and Aspergillus species
(Hodgson, 1998). Self-reported symptoms among co-workers
included fever, headache, rhinitis, coughing, dyspnea
and chest tightness. Chest radiographs were negative and
Stachybotrys-specific serology was
uninformative.
Stachybotrys chartarum, along with
other fungi and environmental tobacco smoke, was
recently postulated to have an association with
pulmonary hemosiderosis in a cluster of Cleveland, Ohio
infants (Montana, 1997; MMWR, 1997)). While SC
was found more frequently in the homes of case infants
compared to controls, exposure of case infants to
mycotoxins in the home could not be determined. Because
there is no field test for airborne mycotoxins, it is
not currently possible to determine if toxins were
actually present in the living space of case infants,
and if so, at what levels. However, since
Stachybotrys chartarum spores containing
mycotoxins have been shown to produce pulmonary
alveolar and intra-bronchiolar inflammation and
hemorrhage in mice (Nikulin, 1996, 1997), more research
into the inhalation effects of these toxins, especially
on immature alveoli and pulmonary vascular walls, is
critically needed.
Pulmonary hemosiderosis is a condition
characterized by recurrent alveolar hemorrhage resulting
in clinical signs of cough, wheeze, hemoptysis,
tachypnea, low grade fever, and microcytic hypochromic
anemia. Chest radiographs typically show patchy
infiltrates and sputum specimens, laryngeal swabs or
gastric aspirates reveal hemosiderin-laden macrophages.
The association of some cases with allergy to cow’s milk
(Heiner syndrome) and its association with
glomerulonephritis in Goodpasture’s syndrome suggests an
immunologic etiology but immunologic findings in
idopathic cases have been inconsistent. Some familial
case reports also suggest a genetic component.
California Department of Health
Services staff reviewed statewide hospital discharge
data for 1989-1995 (last year for which data is
available) and identified a total of eight
hospitalizations and no deaths during these years for
hemosiderosis in infants less than one year of age.
There were no more than 3 cases in any year and no
geographic clustering.
American Academy of Pediatrics
On April 6, 1998, the American Academy
of Pediatrics (AAP) Committee on Environmental Health
released a statement concerning toxic effects of indoor
molds and acute idiopathic pulmonary hemorrhage in
infants. They recommend that until more information is
available on the etiology of this condition,
pediatricians should try to ensure that infants under 1
year of age are not exposed to chronically moldy,
water-damaged environments (AAP, 1998).
Sources of Additional
Information/Assistance:
California Department of Health
Services, Environmental Health Investigations
Branch:
Sandra McNeel, D.V.M.; Debra Gilliss,
M.D., M.P.H.; Richard Kreutzer, M.D.
(510) 622-4500
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