On May 7, 1993, the New York City Department of Health (DOH), the New
York City Human Resources Administration (HRA), and the Mt. Sinai
Occupational Health Clinic convened an expert panel on Stachybotrys
atra in Indoor Environments. The purpose of the panel was to
develop policies for medical and environmental evaluation and
intervention to address Stachybotrys atra (now known as
Stachybotrys chartarum (SC)) contamination. The original guidelines
were developed because of mold growth problems in several New York City
buildings in the early 1990's. This document revises and expands the
original guidelines to include all fungi (mold). It is based both on a
review of the literature regarding fungi and on comments obtained by a
review panel consisting of experts in the fields of microbiology and
health sciences. It is intended for use by building engineers and
management, but is available for general distribution to anyone
concerned about fungal contamination, such as environmental consultants,
health professionals, or the general public.
We are expanding the guidelines to be inclusive of all fungi for
several reasons:
- Many fungi (e.g., species of Aspergillus, Penicillium,
Fusarium, Trichoderma, and Memnoniella) in addition to
SC can produce potent mycotoxins, some of which are identical to
compounds produced by SC. Mycotoxins are fungal metabolites that have
been identified as toxic agents. For this reason, SC cannot be treated
as uniquely toxic in indoor environments.
- People performing renovations/cleaning of widespread fungal
contamination may be at risk for developing Organic Dust Toxic
Syndrome (ODTS) or Hypersensitivity Pneumonitis (HP). ODTS may occur
after a single heavy exposure to dust contaminated with fungi
and produces flu-like symptoms. It differs from HP in that it is not
an immune-mediated disease and does not require repeated exposures to
the same causative agent. A variety of biological agents may cause
ODTS including common species of fungi. HP may occur after repeated
exposures to an allergen and can result in permanent lung damage.
- Fungi can cause allergic reactions. The most common symptoms are
runny nose, eye irritation, cough, congestion, and aggravation of
asthma.
Fungi are present almost everywhere in indoor and outdoor
environments. The most common symptoms of fungal exposure are runny
nose, eye irritation, cough, congestion, and aggravation of asthma.
Although there is evidence documenting severe health effects of fungi in
humans, most of this evidence is derived from ingestion of contaminated
foods (i.e., grain and peanut products) or occupational exposures in
agricultural settings where inhalation exposures were very high. With
the possible exception of remediation to very heavily contaminated
indoor environments, such high-level exposures are not expected to occur
while performing remedial work.
There have been reports linking health effects in office workers to
offices contaminated with moldy surfaces and in residents of homes
contaminated with fungal growth. Symptoms, such as fatigue, respiratory
ailments, and eye irritation were typically observed in these cases.
Some studies have suggested an association between SC and pulmonary
hemorrhage/hemosiderosis in infants, generally those less than six
months old. Pulmonary hemosiderosis is an uncommon condition that
results from bleeding in the lungs. The cause of this condition is
unknown, but may result from a combination of environmental contaminants
and conditions (e.g., smoking, fungal contaminants and other bioaerosols,
and water-damaged homes), and currently its association with SC is
unproven.
The focus of this guidance document addresses mold contamination of
building components (walls, ventilation systems, support beams, etc.)
that are chronically moist or water damaged. Occupants should address
common household sources of mold, such as mold found in bathroom tubs or
between tiles with household cleaners. Moldy food (e.g., breads, fruits,
etc.) should be discarded.
Building materials supporting fungal growth must be remediated as
rapidly as possible in order to ensure a healthy environment.
Repair of the defects that led to water accumulation (or elevated
humidity) should be conducted in conjunction with or prior to fungal
remediation. Specific methods of assessing and remediating fungal
contamination should be based on the extent of visible contamination and
underlying damage. The simplest and most expedient remediation that is
reasonable, and properly and safely removes fungal contamination, should
be used. Remediation and assessment methods are described in this
document.
The use of respiratory protection, gloves, and eye protection is
recommended. Extensive contamination, particularly if heating,
ventilating, air conditioning (HVAC) systems or large occupied spaces
are involved, should be assessed by an experienced health and safety
professional and remediated by personnel with training and experience
handling environmentally contaminated materials. Lesser areas of
contamination can usually be assessed and remediated by building
maintenance personnel. In order to prevent contamination from recurring,
underlying defects causing moisture buildup and water damage must be
addressed. Effective communication with building occupants is an
essential component of all remedial efforts.
Fungi in buildings may cause or exacerbate symptoms of allergies
(such as wheezing, chest tightness, shortness of breath, nasal
congestion, and eye irritation), especially in persons who have a
history of allergic diseases (such as asthma and rhinitis). Individuals
with persistent health problems that appear to be related to fungi or
other bioaerosol exposure should see their physicians for a referral to
practitioners who are trained in occupational/environmental medicine or
related specialties and are knowledgeable about these types of
exposures. Decisions about removing individuals from an affected area
must be based on the results of such medical evaluation, and be made on
a case-by-case basis. Except in cases of widespread fungal contamination
that are linked to illnesses throughout a building, building-wide
evacuation is not indicated.
In summary, prompt remediation of contaminated material and
infrastructure repair is the primary response to fungal contamination in
buildings. Emphasis should be placed on preventing contamination through
proper building and HVAC system maintenance and prompt repair of water
damage.
This document is not a legal mandate and should be used as a
guideline. Currently there are no United States Federal, New York State,
or New York City regulations for evaluating potential health effects of
fungal contamination and remediation. These guidelines are subject to
change as more information regarding fungal contaminants becomes
available.
top of page
On May 7, 1993, the New York City Department of Health (DOH), the New
York City Human Resources Administration (HRA), and the Mt. Sinai
Occupational Health Clinic convened an expert panel on Stachybotrys
atra in Indoor Environments. The purpose of the panel was to
develop policies for medical and environmental evaluation and
intervention to address Stachybotrys atra (now known as
Stachybotrys chartarum (SC)) contamination. The original guidelines
were developed because of mold growth problems in several New York City
buildings in the early 1990's. This document revises and expands the
original guidelines to include all fungi (mold). It is based both on a
review of the literature regarding fungi and on comments obtained by a
review panel consisting of experts in the fields of microbiology and
health sciences. It is intended for use by building engineers and
management, but is available for general distribution to anyone
concerned about fungal contamination, such as environmental consultants,
health professionals, or the general public.
This document contains a discussion of potential health effects;
medical evaluations; environmental assessments; protocols for
remediation; and a discussion of risk communication strategy. The
guidelines are divided into four sections:
1. Health Issues; 2. Environmental Assessment; 3. Remediation; and 4.
Hazard Communication.
We are expanding the guidelines to be inclusive of all fungi for
several reasons:
- Many fungi (e.g., species of Aspergillus, Penicillium,
Fusarium, Trichoderma, and Memnoniella) in addition to
SC can produce potent mycotoxins, some of which are identical to
compounds produced by SC.1, 2, 3, 4
Mycotoxins are fungal metabolites that have been identified as toxic
agents. For this reason, SC cannot be treated as uniquely toxic in
indoor environments.
- People performing renovations/cleaning of widespread fungal
contamination may be at risk for developing Organic Dust Toxic
Syndrome (ODTS) or Hypersensitivity Pneumonitis (HP). ODTS may occur
after a single heavy exposure to dust contaminated with fungi
and produces flu-like symptoms. It differs from HP in that it is not
an immune-mediated disease and does not require repeated exposures to
the same causative agent. A variety of biological agents may cause
ODTS including common species of fungi. HP may occur after repeated
exposures to an allergen and can result in permanent lung damage.5,
6, 7, 8, 9, 10
- Fungi can cause allergic reactions. The most common symptoms are
runny nose, eye irritation, cough, congestion, and aggravation of
asthma.11, 12
Fungi are present almost everywhere in indoor and outdoor
environments. The most common symptoms of fungal exposure are runny
nose, eye irritation, cough, congestion, and aggravation of asthma.
Although there is evidence documenting severe health effects of fungi in
humans, most of this evidence is derived from ingestion of contaminated
foods (i.e., grain and peanut products) or occupational exposures in
agricultural settings where inhalation exposures were very high.13,
14 With the possible exception of remediation to very
heavily contaminated indoor environments, such high level exposures are
not expected to occur while performing remedial work.15
There have been reports linking health effects in office workers to
offices contaminated with moldy surfaces and in residents of homes
contaminated with fungal growth.12, 16, 17, 18, 19, 20
Symptoms, such as fatigue, respiratory ailments, and eye irritation were
typically observed in these cases.
Some studies have suggested an association between SC and pulmonary
hemorrhage/hemosiderosis in infants, generally those less than six
months old. Pulmonary hemosiderosis is an uncommon condition that
results from bleeding in the lungs. The cause of this condition is
unknown, but may result from a combination of environmental contaminants
and conditions (e.g., smoking, other microbial contaminants, and
water-damaged homes), and currently its association with SC is unproven.21,
22, 23
The focus of this guidance document addresses mold contamination of
building components (walls, ventilation systems, support beams, etc.)
that are chronically moist or water damaged. Occupants should address
common household sources of mold, such as mold found in bathroom tubs or
between tiles with household cleaners. Moldy food (e.g., breads, fruits,
etc.) should be discarded.
This document is not a legal mandate and should be used as a
guideline. Currently there are no United States Federal, New York State,
or New York City regulations for evaluating potential health effects of
fungal contamination and remediation. These guidelines are subject to
change as more information regarding fungal contaminants becomes
available.
top of page
1.1 Health Effects
Inhalation of fungal spores, fragments (parts), or metabolites (e.g.,
mycotoxins and volatile organic compounds) from a wide variety of fungi
may lead to or exacerbate immunologic (allergic) reactions, cause toxic
effects, or cause infections.11, 12, 24
There are only a limited number of documented cases of health
problems from indoor exposure to fungi. The intensity of exposure and
health effects seen in studies of fungal exposure in the indoor
environment was typically much less severe than those that were
experienced by agricultural workers but were of a long-term duration.5-10,
12, 14, 16-20, 25-27 Illnesses can result from both high
level, short-term exposures and lower level, long-term exposures. The
most common symptoms reported from exposures in indoor environments are
runny nose, eye irritation, cough, congestion, aggravation of asthma,
headache, and fatigue.11, 12, 16-20
The presence of fungi on building materials as identified by a visual
assessment or by bulk/surface sampling results does not necessitate that
people will be exposed or exhibit health effects. In order for humans to
be exposed indoors, fungal spores, fragments, or metabolites must be
released into the air and inhaled, physically contacted (dermal
exposure), or ingested. Whether or not symptoms develop in people
exposed to fungi depends on the nature of the fungal material (e.g.,
allergenic, toxic, or infectious), the amount of exposure, and the
susceptibility of exposed persons. Susceptibility varies with the
genetic predisposition (e.g., allergic reactions do not always occur in
all individuals), age, state of health, and concurrent exposures. For
these reasons, and because measurements of exposure are not standardized
and biological markers of exposure to fungi are largely unknown, it is
not possible to determine "safe" or "unsafe" levels of exposure for
people in general.
1.1.1 Immunological Effects
Immunological reactions include asthma, HP, and allergic rhinitis.
Contact with fungi may also lead to dermatitis. It is thought that these
conditions are caused by an immune response to fungal agents. The most
common symptoms associated with allergic reactions are runny nose, eye
irritation, cough, congestion, and aggravation of asthma.11,
12 HP may occur after repeated exposures to an allergen
and can result in permanent lung damage. HP has typically been
associated with repeated heavy exposures in agricultural settings but
has also been reported in office settings.25, 26, 27
Exposure to fungi through renovation work may also lead to initiation or
exacerbation of allergic or respiratory symptoms.
1.1.2 Toxic Effects
A wide variety of symptoms have been attributed to the toxic effects
of fungi. Symptoms, such as fatigue, nausea, and headaches, and
respiratory and eye irritation have been reported. Some of the symptoms
related to fungal exposure are non-specific, such as discomfort,
inability to concentrate, and fatigue.11, 12, 16-20
Severe illnesses such as ODTS and pulmonary hemosiderosis have also been
attributed to fungal exposures.5-10, 21, 22
ODTS describes the abrupt onset of fever, flu-like symptoms, and
respiratory symptoms in the hours following a single, heavy
exposure to dust containing organic material including fungi. It differs
from HP in that it is not an immune-mediated disease and does not
require repeated exposures to the same causative agent. ODTS may be
caused by a variety of biological agents including common species of
fungi (e.g., species of Aspergillus and Penicillium).
ODTS has been documented in farm workers handling contaminated material
but is also of concern to workers performing renovation work on building
materials contaminated with fungi.5-10
Some studies have suggested an association between SC and pulmonary
hemorrhage/hemosiderosis in infants, generally those less than six
months old. Pulmonary hemosiderosis is an uncommon condition that
results from bleeding in the lungs. The cause of this condition is
unknown, but may result from a combination of environmental contaminants
and conditions (e.g., smoking, fungal contaminants and other bioaerosols,
and water-damaged homes), and currently its association with SC is
unproven.21, 22, 23
1.1.3 Infectious Disease
Only a small group of fungi have been associated with infectious
disease. Aspergillosis is an infectious disease that can occur in
immunosuppressed persons. Health effects in this population can be
severe. Several species of Aspergillus are known to cause
aspergillosis. The most common is Aspergillus fumigatus.
Exposure to this common mold, even to high concentrations, is unlikely
to cause infection in a healthy person.11, 24
Exposure to fungi associated with bird and bat droppings (e.g.,
Histoplasma capsulatum and Cryptococcus neoformans) can
lead to health effects, usually transient flu-like illnesses, in healthy
individuals. Severe health effects are primarily encountered in
immunocompromised persons.24, 28, 29
1.2 Medical Evaluation
Individuals with persistent health problems that appear to be related
to fungi or other bioaerosol exposure should see their physicians for a
referral to practitioners who are trained in occupational/environmental
medicine or related specialties and are knowledgeable about these types
of exposures. Infants (less than 12 months old) who are experiencing
non-traumatic nosebleeds or are residing in dwellings with damp or moldy
conditions and are experiencing breathing difficulties should receive a
medical evaluation to screen for alveolar hemorrhage. Following this
evaluation, infants who are suspected of having alveolar hemorrhaging
should be referred to a pediatric pulmonologist. Infants diagnosed with
pulmonary hemosiderosis and/or pulmonary hemorrhaging should not be
returned to dwellings until remediation and air testing are completed.
Clinical tests that can determine the source, place, or time of
exposure to fungi or their products are not currently available.
Antibodies developed by exposed persons to fungal agents can only
document that exposure has occurred. Since exposure to fungi routinely
occurs in both outdoor and indoor environments this information is of
limited value.
1.3 Medical Relocation
Infants (less than 12 months old), persons recovering from recent
surgery, or people with immune suppression, asthma, hypersensitivity
pneumonitis, severe allergies, sinusitis, or other chronic inflammatory
lung diseases may be at greater risk for developing health problems
associated with certain fungi. Such persons should be removed from the
affected area during remediation (see Section 3,
Remediation). Persons diagnosed with fungal related diseases should
not be returned to the affected areas until remediation and air testing
are completed.
Except in cases of widespread fungal contamination that are linked to
illnesses throughout a building, a building-wide evacuation is not
indicated. A trained occupational/environmental health practitioner
should base decisions about medical removals in the occupational setting
on the results of a clinical assessment.
top of page
The presence of mold, water damage, or musty odors should be
addressed immediately. In all instances, any source(s) of water must be
stopped and the extent of water damaged determined. Water damaged
materials should be dried and repaired. Mold damaged materials should be
remediated in accordance with this document (see Section 3,
Remediation).
2.1 Visual Inspection
A visual inspection is the most important initial step in identifying
a possible contamination problem. The extent of any water damage and
mold growth should be visually assessed. This assessment is important in
determining remedial strategies. Ventilation systems should also be
visually checked, particularly for damp filters but also for damp
conditions elsewhere in the system and overall cleanliness. Ceiling
tiles, gypsum wallboard (sheetrock), cardboard, paper, and other
cellulosic surfaces should be given careful attention during a visual
inspection. The use of equipment such as a boroscope, to view spaces in
ductwork or behind walls, or a moisture meter, to detect moisture in
building materials, may be helpful in identifying hidden sources of
fungal growth and the extent of water damage.
2.2 Bulk/Surface Sampling
- Bulk or surface sampling is not required to undertake a
remediation. Remediation (as described in Section 3,
Remediation) of visually identified fungal contamination should
proceed without further evaluation.
- Bulk or surface samples may need to be collected to identify
specific fungal contaminants as part of a medical evaluation if
occupants are experiencing symptoms which may be related to fungal
exposure or to identify the presence or absence of mold if a visual
inspection is equivocal (e.g., discoloration, and staining).
- An individual trained in appropriate sampling methodology should
perform bulk or surface sampling. Bulk samples are usually collected
from visibly moldy surfaces by scraping or cutting materials with a
clean tool into a clean plastic bag. Surface samples are usually
collected by wiping a measured area with a sterile swab or by
stripping the suspect surface with clear tape. Surface sampling is
less destructive than bulk sampling. Other sampling methods may also
be available. A laboratory specializing in mycology should be
consulted for specific sampling and delivery instructions.
2.3 Air Monitoring
- Air sampling for fungi should not be part of a routine assessment.
This is because decisions about appropriate remediation strategies can
usually be made on the basis of a visual inspection. In addition,
air-sampling methods for some fungi are prone to false negative
results and therefore cannot be used to definitively rule out
contamination.
- Air monitoring may be necessary if an individual(s) has been
diagnosed with a disease that is or may be associated with a fungal
exposure (e.g., pulmonary hemorrhage/hemosiderosis, and aspergillosis).
- Air monitoring may be necessary if there is evidence from a visual
inspection or bulk sampling that ventilation systems may be
contaminated. The purpose of such air monitoring is to assess the
extent of contamination throughout a building. It is preferable to
conduct sampling while ventilation systems are operating.
- Air monitoring may be necessary if the presence of mold is
suspected (e.g., musty odors) but cannot be identified by a visual
inspection or bulk sampling (e.g., mold growth behind walls). The
purpose of such air monitoring is to determine the location and/or
extent of contamination.
- If air monitoring is performed, for comparative purposes, outdoor
air samples should be collected concurrently at an air intake, if
possible, and at a location representative of outdoor air. For
additional information on air sampling, refer to the American
Conference of Governmental Industrial Hygienists' document, "Bioaerosols:
Assessment and Control."
- Personnel conducting the sampling must be trained in proper air
sampling methods for microbial contaminants. A laboratory specializing
in mycology should be consulted for specific sampling and shipping
instructions.
2.4 Analysis of Environmental Samples
Microscopic identification of the spores/colonies requires
considerable expertise. These services are not routinely available from
commercial laboratories. Documented quality control in the laboratories
used for analysis of the bulk/surface and air samples is necessary. The
American Industrial Hygiene Association (AIHA) offers accreditation to
microbial laboratories (Environmental Microbiology Laboratory
Accreditation Program (EMLAP)). Accredited laboratories must participate
in quarterly proficiency testing (Environmental Microbiology Proficiency
Analytical Testing Program (EMPAT)).
Evaluation of bulk/surface and air sampling data should be performed
by an experienced health professional. The presence of few or trace
amounts of fungal spores in bulk/surface sampling should be considered
background. Amounts greater than this or the presence of fungal
fragments (e.g., hyphae, and conidiophores) may suggest fungal
colonization, growth, and/or accumulation at or near the sampled
location.30 Air samples should be evaluated by
means of comparison (i.e., indoors to outdoors) and by fungal type
(e.g., genera, and species). In general, the levels and types of fungi
found should be similar indoors (in non-problem buildings) as compared
to the outdoor air. Differences in the levels or types of fungi found in
air samples may indicate that moisture sources and resultant fungal
growth may be problematic.
top of page
In all situations, the underlying cause of water accumulation
must be rectified or fungal growth will recur. Any initial
water infiltration should be stopped and cleaned immediately. An
immediate response (within 24 to 48 hours) and thorough clean up,
drying, and/or removal of water damaged materials will prevent or limit
mold growth. If the source of water is elevated humidity, relative
humidity should be maintained at levels below 60% to inhibit mold
growth.31 Emphasis should be on ensuring
proper repairs of the building infrastructure, so that water damage and
moisture buildup does not recur.
Five different levels of abatement are described below. The size of
the area impacted by fungal contamination primarily determines the type
of remediation. The sizing levels below are based on professional
judgement and practicality; currently there is not adequate data to
relate the extent of contamination to frequency or severity of health
effects. The goal of remediation is to remove or clean
contaminated materials in a way that prevents the emission of fungi and
dust contaminated with fungi from leaving a work area and entering an
occupied or non-abatement area, while protecting the health of workers
performing the abatement. The listed remediation methods were
designed to achieve this goal, however, due to the general nature of
these methods it is the responsibility of the people conducting
remediation to ensure the methods enacted are adequate. The listed
remediation methods are not meant to exclude other similarly effective
methods. Any changes to the remediation methods listed in these
guidelines, however, should be carefully considered prior to
implementation.
Non-porous (e.g., metals, glass, and hard plastics) and semi-porous
(e.g., wood, and concrete) materials that are structurally sound and are
visibly moldy can be cleaned and reused. Cleaning should be done using a
detergent solution. Porous materials such as ceiling tiles and
insulation, and wallboards with more than a small area of contamination
should be removed and discarded. Porous materials (e.g., wallboard, and
fabrics) that can be cleaned, can be reused, but should be discarded if
possible. A professional restoration consultant should be contacted when
restoring porous materials with more than a small area of fungal
contamination. All materials to be reused should be dry and visibly free
from mold. Routine inspections should be conducted to confirm the
effectiveness of remediation work.
The use of gaseous, vapor-phase, or aerosolized biocides for remedial
purposes is not recommended. The use of biocides in
this manner can pose health concerns for people in occupied spaces of
the building and for people returning to the treated space if used
improperly. Furthermore, the effectiveness of these treatments is
unproven and does not address the possible health concerns from the
presence of the remaining non-viable mold. For additional information on
the use of biocides for remedial purposes, refer to the American
Conference of Governmental Industrial Hygienists' document, "Bioaerosols:
Assessment and Control."
3.1 Level I: Small Isolated Areas (10 sq.
ft or less) - e.g., ceiling tiles, small areas on walls
- Remediation can be conducted by regular building maintenance
staff. Such persons should receive training on proper clean up
methods, personal protection, and potential health hazards. This
training can be performed as part of a program to comply with the
requirements of the OSHA Hazard Communication Standard (29 CFR
1910.1200).
- Respiratory protection (e.g., N95 disposable respirator), in
accordance with the OSHA respiratory protection standard (29 CFR
1910.134), is recommended. Gloves and eye protection should be worn.
- The work area should be unoccupied. Vacating people from spaces
adjacent to the work area is not necessary but is recommended in the
presence of infants (less than 12 months old), persons recovering from
recent surgery, immune suppressed people, or people with chronic
inflammatory lung diseases (e.g., asthma, hypersensitivity pneumonitis,
and severe allergies).
- Containment of the work area is not necessary. Dust suppression
methods, such as misting (not soaking) surfaces prior to remediation,
are recommended.
- Contaminated materials that cannot be cleaned should be removed
from the building in a sealed plastic bag. There are no special
requirements for the disposal of moldy materials.
- The work area and areas used by remedial workers for egress should
be cleaned with a damp cloth and/or mop and a detergent solution.
- All areas should be left dry and visibly free from contamination
and debris.
3.2 Level II: Mid-Sized Isolated Areas (10
- 30 sq. ft.) - e.g., individual wallboard panels.
- Remediation can be conducted by regular building maintenance
staff. Such persons should receive training on proper clean up
methods, personal protection, and potential health hazards. This
training can be performed as part of a program to comply with the
requirements of the OSHA Hazard Communication Standard (29 CFR
1910.1200).
- Respiratory protection (e.g., N95 disposable respirator), in
accordance with the OSHA respiratory protection standard (29 CFR
1910.134), is recommended. Gloves and eye protection should be worn.
- The work area should be unoccupied. Vacating people from spaces
adjacent to the work area is not necessary but is recommended in the
presence of infants (less than 12 months old), persons having
undergone recent surgery, immune suppressed people, or people with
chronic inflammatory lung diseases (e.g., asthma, hypersensitivity
pneumonitis, and severe allergies).
- The work area should be covered with a plastic sheet(s) and sealed
with tape before remediation, to contain dust/debris.
- Dust suppression methods, such as misting (not soaking) surfaces
prior to remediation, are recommended.
- Contaminated materials that cannot be cleaned should be removed
from the building in sealed plastic bags. There are no special
requirements for the disposal of moldy materials.
- The work area and areas used by remedial workers for egress should
be HEPA vacuumed (a vacuum equipped with a High-Efficiency Particulate
Air filter) and cleaned with a damp cloth and/or mop and a detergent
solution.
- All areas should be left dry and visibly free from contamination
and debris.
3.3 Level III: Large Isolated Areas (30 -
100 square feet) - e.g., several wallboard panels.
A health and safety professional with experience performing microbial
investigations should be consulted prior to remediation activities to
provide oversight for the project.
The following procedures at a minimum are recommended:
- Personnel trained in the handling of hazardous materials and
equipped with respiratory protection, (e.g., N95 disposable
respirator), in accordance with the OSHA respiratory protection
standard (29 CFR 1910.134), is recommended. Gloves and eye protection
should be worn.
- The work area and areas directly adjacent should be covered with a
plastic sheet(s) and taped before remediation, to contain dust/debris.
- Seal ventilation ducts/grills in the work area and areas directly
adjacent with plastic sheeting.
- The work area and areas directly adjacent should be unoccupied.
Further vacating of people from spaces near the work area is
recommended in the presence of infants (less than 12 months old),
persons having undergone recent surgery, immune suppressed people, or
people with chronic inflammatory lung diseases (e.g., asthma,
hypersensitivity pneumonitis, and severe allergies).
- Dust suppression methods, such as misting (not soaking) surfaces
prior to remediation, are recommended.
- Contaminated materials that cannot be cleaned should be removed
from the building in sealed plastic bags. There are no special
requirements for the disposal of moldy materials.
- The work area and surrounding areas should be HEPA vacuumed and
cleaned with a damp cloth and/or mop and a detergent solution.
- All areas should be left dry and visibly free from contamination
and debris.
If abatement procedures are expected to generate a lot of dust (e.g.,
abrasive cleaning of contaminated surfaces, demolition of plaster walls)
or the visible concentration of the fungi is heavy (blanket coverage as
opposed to patchy), then it is recommended that the remediation
procedures for Level IV are followed.
3.4 Level IV: Extensive Contamination
(greater than 100 contiguous square feet in an area)
A health and safety professional with experience performing microbial
investigations should be consulted prior to remediation activities to
provide oversight for the project. The following procedures are
recommended:
- Personnel trained in the handling of hazardous materials equipped
with:
- Full-face respirators with high efficiency particulate air (HEPA)
cartridges
- Disposable protective clothing covering both head and shoes
- Gloves
- Containment of the affected area:
- Complete isolation of work area from occupied spaces using
plastic sheeting sealed with duct tape (including ventilation
ducts/grills, fixtures, and any other openings)
- The use of an exhaust fan with a HEPA filter to generate
negative pressurization
- Airlocks and decontamination room
- Vacating people from spaces adjacent to the work area is not
necessary but is recommended in the presence of infants (less than 12
months old), persons having undergone recent surgery, immune
suppressed people, or people with chronic inflammatory lung diseases
(e.g., asthma, hypersensitivity pneumonitis, and severe allergies).
- Contaminated materials that cannot be cleaned should be removed
from the building in sealed plastic bags. The outside of the bags
should be cleaned with a damp cloth and a detergent solution or HEPA
vacuumed in the decontamination chamber prior to their transport to
uncontaminated areas of the building. There are no special
requirements for the disposal of moldy materials.
- The contained area and decontamination room should be HEPA
vacuumed and cleaned with a damp cloth and/or mop with a detergent
solution and be visibly clean prior to the removal of isolation
Makiiers.
- Air monitoring should be conducted prior to occupancy to determine
if the area is fit to reoccupy.
3.5 Level V: Remediation of HVAC Systems
3.5.1 A Small Isolated Area of Contamination (<10 square
feet) in the HVAC System
- Remediation can be conducted by regular building maintenance
staff. Such persons should receive training on proper clean up
methods, personal protection, and potential health hazards. This
training can be performed as part of a program to comply with the
requirements of the OSHA Hazard Communication Standard (29 CFR
1910.1200).
- Respiratory protection (e.g., N95 disposable respirator), in
accordance with the OSHA respiratory protection standard (29 CFR
1910.134), is recommended. Gloves and eye protection should be worn.
- The HVAC system should be shut down prior to any remedial
activities.
- The work area should be covered with a plastic sheet(s) and sealed
with tape before remediation, to contain dust/debris.
- Dust suppression methods, such as misting (not soaking) surfaces
prior to remediation, are recommended.
- Growth supporting materials that are contaminated, such as the
paper on the insulation of interior lined ducts and filters, should be
removed. Other contaminated materials that cannot be cleaned should be
removed in sealed plastic bags. There are no special requirements for
the disposal of moldy materials.
- The work area and areas immediately surrounding the work area
should be HEPA vacuumed and cleaned with a damp cloth and/or mop and a
detergent solution.
- All areas should be left dry and visibly free from contamination
and debris.
- A variety of biocides are recommended by HVAC manufacturers for
use with HVAC components, such as, cooling coils and condensation
pans. HVAC manufacturers should be consulted for the products they
recommend for use in their systems.
3.5.2 Areas of Contamination (>10 square feet) in the HVAC
System
A health and safety professional with experience performing microbial
investigations should be consulted prior to remediation activities to
provide oversight for remediation projects involving more than a small
isolated area in an HVAC system. The following procedures are
recommended:
- Personnel trained in the handling of hazardous materials equipped
with:
- Respiratory protection (e.g., N95 disposable respirator), in
accordance with the OSHA respiratory protection standard (29 CFR
1910.134), is recommended.
- Gloves and eye protection
- Full-face respirators with HEPA cartridges and disposable
protective clothing covering both head and shoes should be worn if
contamination is greater than 30 square feet.
- The HVAC system should be shut down prior to any remedial
activities.
- Containment of the affected area:
- Complete isolation of work area from the other areas of the HVAC
system using plastic sheeting sealed with duct tape.
- The use of an exhaust fan with a HEPA filter to generate
negative pressurization.
- Airlocks and decontamination room if contamination is greater
than 30 square feet.
- Growth supporting materials that are contaminated, such as the
paper on the insulation of interior lined ducts and filters, should be
removed. Other contaminated materials that cannot be cleaned should be
removed in sealed plastic bags. When a decontamination chamber is
present, the outside of the bags should be cleaned with a damp cloth
and a detergent solution or HEPA vacuumed prior to their transport to
uncontaminated areas of the building. There are no special
requirements for the disposal of moldy materials.
- The contained area and decontamination room should be HEPA
vacuumed and cleaned with a damp cloth and/or mop and a detergent
solution prior to the removal of isolation Makiiers.
- All areas should be left dry and visibly free from contamination
and debris.
- Air monitoring should be conducted prior to re-occupancy with the
HVAC system in operation to determine if the area(s) served by the
system are fit to reoccupy.
- A variety of biocides are recommended by HVAC manufacturers for
use with HVAC components, such as, cooling coils and condensation
pans. HVAC manufacturers should be consulted for the products they
recommend for use in their systems.
top of page
When fungal growth requiring large-scale remediation is found, the
building owner, management, and/or employer should notify occupants in
the affected area(s) of its presence. Notification should include a
description of the remedial measures to be taken and a timetable for
completion. Group meetings held before and after remediation with full
disclosure of plans and results can be an effective communication
mechanism. Individuals with persistent health problems that appear to be
related to bioaerosol exposure should see their physicians for a
referral to practitioners who are trained in occupational/environmental
medicine or related specialties and are knowledgeable about these types
of exposures. Individuals seeking medical attention should be provided
with a copy of all inspection results and interpretation to give to
their medical practitioners.
top of page
In summary, the prompt remediation of contaminated material and
infrastructure repair must be the primary response to fungal
contamination in buildings. The simplest and most expedient remediation
that properly and safely removes fungal growth from buildings should be
used. In all situations, the underlying cause of water accumulation must
be rectified or the fungal growth will recur. Emphasis should be placed
on preventing contamination through proper building maintenance and
prompt repair of water damaged areas.
Widespread contamination poses much larger problems that must be
addressed on a case-by-case basis in consultation with a health and
safety specialist. Effective communication with building occupants is an
essential component of all remedial efforts. Individuals with persistent
health problems should see their physicians for a referral to
practitioners who are trained in occupational/environmental medicine or
related specialties and are knowledgeable about these types of
exposures.
top of page
- Bata A, Harrach B, Kalman U, Kis-tamas A, Lasztity R. Macrocyclic
Trichothecene Toxins Produced by Stachybotrys atra Strains
Isolated in Middle Europe. Applied and Environmental Microbiology
1985; 49:678-81.
- Jarvis B, "Mycotoxins and Indoor Air Quality," Biological
Contaminants in Indoor Environments, ASTM STP 1071, Morey P,
Feely Sr. J, Otten J, Editors, American Society for Testing and
Materials, Philadelphia, 1990.
- Yang C, Johanning E, "Airborne Fungi and Mycotoxins," Manual
of Environmental Microbiology, Hurst C, Editor in Chief, ASM
Press, Washington, D.C., 1996
- Jarvis B, Mazzola E. Macrocyclic and Other Novel Trichothecenes:
Their Structure, Synthesis, and Biological Significance. Acc.
Chem. Res. 1982; 15:388-95.
- Von Essen S, Robbins R, Thompson A, Rennard S. Organic Dust Toxic
Syndrome: An Acute Febrile Reaction to Organic Dust Exposure Distinct
from Hypersensitivity Pneumonitis. Clinical Toxicology 1990;
28(4):389-420.
- Richerson H. Unifying Concepts Underlying the Effects of Organic
Dust Exposures. American Journal of Industrial Medicine 1990;
17:139-42.
- Malmberg P, Rask-Andersen A, Lundholm M, Palmgren U. Can Spores
from Molds and Actinomycetes Cause an Organic Dust Toxic Syndrome
Reaction?. American Journal of Industrial Medicine 1990;
17:109-10.
- Malmberg P. Health Effects of Organic Dust Exposure in Dairy
Farmers. American Journal of Industrial Medicine 1990;
17:7-15.
- Yoshida K, Masayuki A, Shukuro A. Acute Pulmonary Edema in a
Storehouse of Moldy Oranges: A Severe Case of the Organic Dust Toxic
Syndrome. Archives of Environmental Health 1989;
44(6): 382-84.
- Lecours R, Laviolette M, Cormier Y. Bronchoalveolar Lavage in
Pulmonary Mycotoxicosis. Thorax 1986; 41:924-6.
- Levetin E. "Fungi," Bioaerosols, Burge H, Editor, CRC
Press, Boca Raton, Florida, 1995.
- Husman T. Health Effects of Indoor-air Microorganisms. Scand J
Work Environ Health 1996; 22:5-13.
- Miller J D. Fungi and Mycotoxins in Grain: Implications for Stored
Product Research. J Stored Prod Res 1995; 31(1):1-16.
- Cookingham C, Solomon W. "Bioaerosol-Induced Hypersensitivity
Diseases," Bioaerosols, Burge H, Editor, CRC Press, Boca
Raton, Florida, 1995.
- Rautiala S, Reponen T, Nevalainen A, Husman T, Kalliokoski P.
Control of Exposure to Airborne Viable Microorganisms During
Remediation of Moldy Buildings; Report of Three Case Studies.
American Industrial Hygiene Association Journal 1998; 59:455-60.
- Dales R, Zwanenburg H, Burnett R, Franklin C. Respiratory Health
Effects of Home Dampness and Molds among Canadian Children.
American Journal of Epidemiology 1991; 134(2):
196-203.
- Hodgson M, Morey P, Leung W, Morrow L, Miller J D, Jarvis B,
Robbins H, Halsey J, Storey E. Building-Associated Pulmonary Disease
from Exposure to Stachybotrys chartarum and Aspergillus
versicolor. Journal of Occupational and Environmental
Medicine 1998; 40(3)241-9.
- Croft W, Jarvis B, Yatawara C. Airborne Outbreak of Trichothecene
Toxicosis. Atmospheric Environment 1986; 20(3)549-52.
- DeKoster J, Thorne P. Bioaerosol Concentrations in Noncomplaint,
Complaint, and Intervention Homes in the Midwest. American
Industrial Hygiene Association Journal 1995; 56:573-80.
- Johanning E, Biagini R, Hull D, Morey P, Jarvis B, Landbergis P.
Health and Immunological Study Following Exposure to Toxigenic Fungi
(Stachybotrys chartarum) in a Water-Damaged Office
Environment. Int Arch Occup Environ Health 1996; 68:207-18.
- Montana E, Etzel R, Allan T, Horgan T, Dearborn D. Environmental
Risk Factor Associated with Pediatric Idiopathic Pulmonary Hemorrhage
and Hemosiderosis in a Cleveland Community. Pediatrics 1997;
99(1)
- Etzel R, Montana E, Sorenson W G, Kullman G, Allan T, Dearborn D.
Acute Pulmonary Hemorrhage in Infants Associated with Exposure to
Stachybotrys atra and Other Fungi. Ach Pediatr Adolesc Med
1998; 152:757-62.
- CDC. Update: Pulmonary Hemorrhage/Hemosiderosis Among Infants ---
Cleveland, Ohio, 1993 - 1996. MMWR 2000; 49(9):
180-4.
- Burge H, Otten J. "Fungi," Bioaerosols Assessment and Control,
Macher J, Editor, American Conference of Industrial Hygienists,
Cincinnati, Ohio, 1999.
- do Pico G. Hazardous Exposure and Lung Disease Among Farm Workers.
Clinics in Chest Medicine 1992; 13(2):311-28.
- Hodgson M, Morey P, Attfield M, Sorenson W, Fink J, Rhodes W,
Visvesvara G. Pulmonary Disease Associated with Cafeteria Flooding.
Archives of Environmental Health 1985; 40(2):96-101.
- Weltermann B, Hodgson M, Storey E, DeGraff, Jr. A, Bracker A,
Groseclose S, Cole S, Cartter M, Phillips D. Hypersensitivity
Pneumonitis: A Sentinel Event Investigation in a Wet Building.
American Journal of Industrial Medicine 1998; 34:499-505.
- Band J. "Histoplasmosis," Occupational Respiratory Diseases,
Merchant J, Editor, U.S. Department of Health and Human Services,
Washington D.C., 1986.
- Bertolini R. "Histoplasmosis A Summary of the Occupational Health
Concern," Canadian Centre for Occupational Health and Safety.
Hamilton, Ontario, Canada, 1988.
- Yang C. P&K Microbiology Services, Inc. Microscopic Examination of
Sticky Tape or Bulk Samples for the Evaluation and Identification of
Fungi. Cherry Hill, New Jersey.
- American Society of Heating, Refrigerating and Air-Conditioning
Engineers, Inc. Thermal Environmental Conditions for Human Occupancy -
ASHRAE Standard (ANSI/ASHRAE 55-1992). Atlanta, Georgia, 1992.
top of page
The New York City Department of Health would like to thank the
following individuals and organizations for participating in the
revision of these guidelines. Please note that these guidelines do not
necessarily reflect the opinions of the participants nor their
organizations.
| Name |
|
Company/Institution |
| Dr. Susan Klitzman |
|
Hunter College |
| Dr. Philip Morey |
|
AQS Services, Inc |
| Dr. Donald Ahearn |
|
Georgia State University |
| Dr. Sidney Crow |
|
Georgia State University |
| Dr. J. David Miller |
|
Carleton University |
| Dr. Bruce Jarvis |
|
University of Maryland at College Park |
| Mr. Ed Light |
|
Building Dynamics, LLC |
| Dr. Chin Yang |
|
P&K Microbiology Services, Inc |
| Dr. Harriet Burge |
|
Harvard School of Public Health |
| Dr. Dorr Dearborn |
|
Rainbow Children's Hospital |
| Mr. Eric Esswein |
|
National Institute for Occupational
Safety and Health |
| Dr. Ed Horn |
|
The New York State Department of
Health |
| Dr. Judith Schreiber |
|
The New York State Department of
Health |
| Mr. Gregg Recer |
|
The New York State Department of
Health |
| Dr. Gerald Llewellyn |
|
State of Delaware, Division of Public
Health |
| Mr. Daniel Price |
|
Interface Research Corporation |
| Ms. Sylvia Pryce |
|
The NYC Citywide Office of
Occupational Safety and Health |
| Mr. Armando Chamorro |
|
Ambient Environmental |
| Ms. Marie-Alix d'Halewyn |
|
Laboratoire de santι publique du
Quιbec |
| Dr. Elissa A. Favata |
|
Environmental and Occupational Health
Associates |
| Dr. Harriet Ammann |
|
Washington State Department of Health |
| Mr. Terry Allan |
|
Cuyahoga County Board of Health |
We would also like to thank the many others who offered opinions,
comments, and assistance at various stages during the development of
these guidelines.
Christopher D'Andrea, M.S. of the Environmental and Occupational
Disease Epidemiology Unit, was the editor of this document.
For further information regarding this document please contact the
New York City Department of Health at (212) 788-4290 / 4288.