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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
REFERENCES
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CDC. "Update: pulmonary hemorrhage/hemosiderosis
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