ArticlePDF Available

Issues Affecting Respirator Selection for Workers Exposed to Infectious Aerosols: Emphasis on Healthcare Settings

Authors:

Abstract

The goal of occupational health practice is to protect the health of workers by preventing diseases and injuries from occurring. When work activities are anticipated, recognized, or found during an investigation to involve risks to workers' health, preventive measures should be taken to control hazardous exposures in the workplace. Respirators are often used to control inhalational exposures to hazardous airborne contaminants, including infectious agents. Of the three methods available for selecting a respirator, the expert opinion method is used most frequently to recommend respirators for controlling exposures to infectious agents. The size of the particles comprising an infectious aerosol has received particular attention relating to the selection of respiratory protection for healthcare workers. Conflicting meanings of the term “droplet” are central to this issue and may be partly responsible for confusion concerning the particle sizes that surgical masks are unlikely to protect against. Although workers caring for patients with contagious respiratory infections are at risk of exposure to large-particle droplets greater than 100 micrometers in diameter, their risks of inhalational exposure to infectious particles are likely to be predominantly to an aerosol consisting of a mixture of evaporating droplets and droplet nuclei that remain suspended in room air for prolonged periods. Because surgical masks are intended to be used only as barriers against large-particle droplets, only respirators certified by the National Institute for Occupational Safety and Health should be used as part of a strategy for protecting workers against inhalational exposures to infectious aerosols. The issues outlined in this paper are focused on workers in healthcare settings, but also apply in other settings where workers may be exposed to infectious aerosols.
20
Abstract
The goal of occupational health practice is to pro-
tect the health of workers by preventing diseases and
injuries from occurring. When work activities are an-
ticipated, recognized, or found during an investigation
to involve risks to workers’ health, preventive measures
should be taken to control hazardous exposures in the
workplace. Respirators are often used to control inha-
lational exposures to hazardous airborne contaminants,
including infectious agents. Of the three methods avail-
able for selecting a respirator, the expert opinion
method is used most frequently to recommend respira-
tors for controlling exposures to infectious agents. The
size of the particles comprising an infectious aerosol
has received particular attention relating to the selection
of respiratory protection for healthcare workers. Con-
flicting meanings of the term droplet” are central to
this issue and may be partly responsible for confusion
concerning the particle sizes that surgical masks are
unlikely to protect against. Although workers caring
for patients with contagious respiratory infections are
at risk of exposure to large-particle droplets greater
than 100 micrometers in diameter, their risks of inhala-
tional exposure to infectious particles are likely to be
predominantly to an aerosol consisting of a mixture of
evaporating droplets and droplet nuclei that remain sus-
pended in room air for prolonged periods. Because sur-
gical masks are intended to be used only as barriers
against large-particle droplets, only respirators certified
by the National Institute for Occupational Safety and
Health should be used as part of a strategy for protect-
ing workers against inhalational exposures to infectious
aerosols. The issues outlined in this paper are focused
on workers in healthcare settings, but also apply in
other settings where workers may be exposed to infec-
tious aerosols.
Introduction
The primary goal of occupational health practice
is to protect the health of workers by preventing dis-
eases and injuries from occurring (International
Commission on Occupational Health, 2002). When
work activities are anticipated, recognized, or found
during an investigation (e.g., an outbreak of an infec-
tious disease) to involve risks to workers’ health, pre-
ventive measures should be taken to control hazard-
ous exposures. Respirators are often selected as a
means of reducing workers’ inhalational risks when
engineering controls or administrative measures are
insufficient or unavailable for controlling exposures
to hazardous airborne contaminants, including infec-
tious agents. Several different types of respirators
provide varying levels of protection; each type has
different characteristics, advantages, and disadvan-
tages. Knowledge of how to select a respirator is es-
sential for ensuring that a worker’s health is pro-
tected.
Applied Biosafety, 9(1) pp. 20-36 © ABSA 2004
Article
Issues Affecting Respirator Selection for
Workers Exposed to Infectious Aerosols:
Emphasis on Healthcare Settings
Steven W. Lenhart1, Teresa Seitz1, Douglas Trout1, and Nancy Bollinger2
1Centers for Disease Control and Prevention, National Institute for Occupational Safety and Health, Cincinnati, Ohio;
and 2Centers for Disease Control and Prevention, National Institute for Occupational Safety and Health, Morgantown,
West Virginia
21
The purpose of this article is to review issues
affecting the selection of respirators for reducing
workers’ exposures to infectious aerosols. Aerosols
are dispersions of liquid or solid particles suspended
in air (Baron & Willeke, 2001, p. 1065), and infec-
tious aerosols are defined as dispersions of airborne
particles capable of causing infection. Methods that
can be used to make a respirator selection are ad-
dressed first; three selection methods are described.
Next, characteristics of infectious particles and the
potential for airborne spread of infectious agents in
healthcare settings are discussed. These issues are
important to understanding how to determine the
potential effectiveness of respirators in minimizing
exposures to infectious aerosols. Finally, information
is provided demonstrating why surgical masks
should not be worn as protection against infectious
aerosols.
Respirator Selection Methods
Once a decision has been made that respirators
are needed to protect the health of workers, the
process of selecting an appropriate respirator re-
quires an understanding of the work activities associ-
ated with potential exposures, the health effects of
overexposure, properties of the air contaminant
(e.g., in healthcare settings, the characteristics and
behavior of an aerosolized infectious disease agent),
and worker and workplace factors that may affect
how effective a respirator will be in protecting work-
ers (Johnson, 2001; McCullough & Brosseau, 1999).
In addition, consideration must be given to whether
wearing a certain type of respirator will adversely
affect a worker’s ability to perform his or her tasks or
will create a risk to the safety of the worker or others
(e.g., the trailing hose of a supplied air respirator can
be a tripping hazard). These latter issues should be
addressed by considering the advantages and disad-
vantages of the various types of respirators from
which a choice must be made. Table 1 provides ex-
amples of the advantages and disadvantages of differ-
ent types of respirators as they relate to potential
infectious aerosol exposures in healthcare settings.
Because different types of respirators provide
varying levels of protection, having information that
compares their relative protective capabilities is es-
sential when making a selection. This is one of the
functions of an assigned protection factor (APF), a
unitless value that historically has been defined as
representing the minimum level of protection that a
respirator class can be anticipated to provide for a
substantial proportion (usually 95%) of properly fit-
ted and trained respirator users (Guy, 1985; Myers,
Lenhart, Campbell, & Provost, 1983). For example,
an assigned protection factor of 50 means that a res-
pirator having this value will reduce most wearers’
exposures to a contaminant to 2% [(1/APF) x 100%
= 2%] of what they would have been exposed to if
they had not been wearing a respirator—a 98% expo-
sure reduction.
In 2003, the Occupational Safety and Health
Administration (OSHA) proposed the following
definition of assigned protection factor: the work-
place level of respiratory protection that a respirator
or class of respirators is expected to provide to em-
ployees when the employer implements a continu-
ing, effective respiratory protection program as speci-
fied by Title 29 CFR 1901.134 (Occupational Safety
and Health Administration [OSHA], 2003). As-
signed protection factors range from 10 for fit-tested,
air-purifying, half-facepiece respirators to 10,000 for
pressure demand self-contained breathing appara-
tuses (American National Standards Institute
[ANSI], 1992; McCullough & Brosseau, 1999; Na-
tional Institute for Occupational Safety and Health
[NIOSH], 1987; OSHA, 2003).
Choosing a selection method is the first impor-
tant decision in a respirator selection process. The
choices are the hazard ratio method, the risk analysis
method, and the expert opinion method.
Hazard Ratio Method
The hazard ratio method, or the industrial hy-
giene method, is a quantitative method used most
commonly to select respirators for noninfectious
aerosols, gases, and vapors. Using this method re-
quires estimates of the air concentrations of a con-
taminant measured during a person’s work activities
and knowledge of the established (or recommended)
occupational exposure limits of that contaminant. A
minimum level of respiratory protection is calculated
by dividing the highest air concentration measure-
ment by the most protective occupational exposure
Lenhart / Seitz / Trout / Bollinger
22
Respirator Type Advantages Disadvantages
Filtering Facepiece Respirator
Assigned protection factor = 10;
better-performing models, if fit
tested and used properly, reduce
respiratory exposure to 10% of what
it would be without the respirator.
yLightweight.
yNo maintenance, cleaning, or
disinfection needed.
yNo effect on mobility.
yOnly respirator type with models
available without an exhalation
valve. A healthcare worker can wear
such a respirator to protect patients
and others from expired aerosols of
the healthcare worker.
yProvides no eye protection.
yCan add to heat burden.
yInward leakage at gaps in face seal.
yDifficult for a user to do a seal check.
yLevel of protection varies greatly among models.
yCommunication may be difficult.
yFit testing required to select proper facepiece size.
ySome eyewear may interfere with the fit.
Elastomeric Half-facepiece Respirator
Assigned protection factor = 10;
most models, if fit tested and used
properly, reduce respiratory
exposure to 10% or less of what it
would be without the respirator.
yLow maintenance.
yReusable facepiece and replaceable
filters and cartridges.
yNo effect on mobility.
yProvides no eye protection.
yCan add to heat burden.
yFacepiece must be cleaned and disinfected before reuse,
which may place workers at risk of contact exposure.
yInward leakage at gaps in face seal.
yCommunication may be difficult.
yFit testing required to select proper facepiece size.
ySome eyewear may interfere with the fit.
Elastomeric Full-facepiece Respirator
Assigned protection factor = 50;
most models, if fit tested and used
properly, reduce respiratory
exposure to 2% or less of what it
would be without the respirator.
yProvides eye protection.
yLow maintenance.
yReusable facepiece and replaceable
filters and cartridges.
yNo effect on mobility.
yMore effective face seal than that of
filtering facepiece or elastomeric
half-facepiece respirators.
yCan add to heat burden.
yDiminished field-of-vision compared to half-facepiece.
yFacepiece must be cleaned and disinfected before reuse,
which may place workers at risk of contact exposure.
yInward leakage at gaps in face seal.
yFit testing required to select proper facepiece size.
yCommunication may be difficult.
yMust be quantitatively fit tested to reduce exposures to 2%.
yFacepiece lens can fog without nose cup or lens treatment.
ySpectacle kit needed for people who wear corrective glasses.
Powered Air-purifying Respirator with Hood, Helmet, or Loose-fitting Facepiece
Assigned protection factor = 25;
most models, if used properly,
reduce respiratory exposure to 4%
or less of what it would be without
the respirator.
yProtection for people with beards,
missing dentures, or facial scars.
yProvides eye protection.
yLow breathing resistance.
yFlowing air creates cooling effect.
yFace seal leakage is generally outward.
yFit testing is not required.
yPrescription glasses can be worn.
yHoods completely cover head and
neck and may also cover shoulders
and torso, providing extensive
barrier protection.
yCommunication less difficult than
with elastomeric half-facepiece or
full-facepiece respirators.
yReusable components and
replaceable filters.
yAdded weight of battery and blower.
yAwkward for some tasks.
yComponents must be cleaned and disinfected before
reuse, which may place other workers at risk for contact
exposure.
yBattery requires charging.
yNoise from a device’s blower may make stethoscope use
difficult.
yAir flow must be tested with flow device before use.
Table 1
Advantages and disadvantages of different respirator types as they
relate to potential infectious aerosol exposures in healthcare settings.
23
Powered Air-purifying Respirator with Tight-fitting Half-facepiece or Full-facepiece
Assigned protection factor = 50;
most models, if used properly,
reduce respiratory exposure to 2%
or less of what it would be without
the respirator.
yProvides eye protection with full-
facepiece.
yLow breathing resistance.
yFlowing air creates cooling effect.
yFace seal leakage is generally
outward.
yReusable components and
replaceable filters.
yAdded weight of battery and blower.
yAwkward for some tasks.
yNo eye protection with half-facepiece.
yComponents must be cleaned and disinfected before
reuse, which may place other workers at risk for contact
exposure.
yFit testing required to select proper facepiece size.
yBattery requires charging.
yNoise from a device’s blower may make stethoscope use
difficult.
yCommunication may be difficult.
ySpectacle kit needed for people who wear corrective
glasses with full-facepiece respirators.
yAir flow must be tested with flow device before use.
Supplied Air Respirator
The three modes of operation of
supplied air respirators are demand
(negative pressure), continuous
flow, and pressure demand.
Pressure demand, full-facepiece
models (assigned protection factor =
2,000), if fit tested and used
properly, reduce respiratory
exposure to 0.05% or less of what it
would be without the respirator.
yProvides eye protection with full-
facepiece or hood.
yDoes not depend on filters to purify
ambient air.
yLow breathing resistance.
yFace seal leakage is outward.
yFlowing air creates cooling effect.
yMobility limited to air-supply hose length and proximity
of the air supply.
yTrailing hose may be a tripping hazard and may get in
the way of gurneys and other medical equipment on
wheels.
yFit testing required to select proper facepiece size.
yComponents must be cleaned and disinfected before
reuse, which may place other workers at risk for contact
exposure.
yCommunication may be difficult.
ySource of pressure-regulated Grade D breathing air
needed.
ySource of breathing air must be tested to ensure quality.
Self-contained Breathing Apparatus (SCBA)
Assigned protection factor =
10,000; pressure demand, full-
facepiece models, if fit tested and
used properly, reduce respiratory
exposure to 0.01% or less of what it
would be without the respirator.
yProvides eye protection.
yFace seal leakage is outward.
yDoes not depend on filters or
cartridges to purify ambient air.
yFlowing air creates cooling effect.
yDuration of use limited by service life of air cylinders.
yFrequent work stoppages needed to change air
cylinders.
yFit testing required to select proper facepiece size.
ySCBA weigh as much as 40 pounds.
yComponents must be cleaned and disinfected before
reuse, which may place other workers at risk for contact
exposure.
yCommunication may be difficult.
ySupply of replacement air cylinders needed.
yFacility needed to recharge empty air bottles.
ySource of breathing air must be tested to ensure quality.
ySCBA must be returned annually or every 3 years
depending on manufacturer for inspection and repair.
Table 1 (Continued)
Advantages and disadvantages of different respirator types as they
relate to potential infectious aerosol exposures in healthcare settings.
Respirator Type Advantages Disadvantages
Lenhart / Seitz / Trout / Bollinger
24
Issues Affecting Respirator Selection for Workers Exposed to Infectious Aerosols
limit of the contaminant. A respirator from the res-
pirator class having an assigned protection factor
equal to or exceeding this value would then be se-
lected. However, applying this method to respirator
selection decisions for infectious aerosols is difficult
and often impossible.
Two major obstacles limit application of the haz-
ard ratio method to worker exposures to infectious
agents. The first involves uncertainties about the air
concentrations of infectious agents (due in part to
difficulties in sampling air for viable infectious
agents). Second, neither occupational exposure lim-
its nor guidelines for infectious agents are generally
available. This is because the infectious inhalation
dose of most disease agents is poorly characterized
and may extend over a considerable range because of
variations in host susceptibility and related factors.
According to the OSHA respiratory protection stan-
dard (Title 29 CFR 1910.134), when exposures can-
not be reasonably estimated, an employer is required
to consider the work environment as immediately
dangerous to life or health and to provide to employ-
ees either a self-contained breathing apparatus
(SCBA) or a combination supplied-air respirator
with an auxiliary SCBA (OSHA, 1998b). Both of
these types of respirators would be impractical for
use in many work settings, including healthcare.
(Advantages and disadvantages of these respirator
types are described in Table 1.) However, OSHA did
not intend that only these two respirator types could
be selected when workplace-specific exposure meas-
urements did not exist. Rather, OSHA intended that
professional judgment also be used to evaluate all
factors associated with making a respirator selection
and that the most protective respirators needed to be
selected only when a less protective respirator could
not confidently be presumed safe (OSHA, 1998a).
Risk Analysis Method
The risk analysis method of making a respirator
selection is a quantitative modeling approach in
which cumulative risk is calculated. This method has
been applied to respirator selections for protecting
against inhalational exposures to Bacillus anthracis
spores (as a possible bioterrorism agent [Nicas &
Hubbard, 2003; Nicas, Neuhaus, & Spear, 2000]),
Mycobacterium tuberculosis (Nicas, 1995, 1996), and
Coccidioides immitis (Nicas & Hubbard, 2002).
The data used to compute the cumulative risk of
an infectious aerosol are estimates of the infectious
inhalational dose of an infectious agent, the air con-
centration of infectious particles, the respirator
user’s breathing rate, the fractional penetration value
of the user’s respirator, the duration of a respirator
use period, and the number of respirator use periods
(Nicas & Hubbard, 2002, 2003; Nicas et al., 2000).
Limitations of this method are that complete infor-
mation is seldom available, and, as is true when ap-
plying the hazard ratio method to infectious aero-
sols, that important data—the infectious inhalational
dose and the air concentrations of infectious parti-
cles to which workers may be exposed—are usually
quite uncertain. However, advantages of the method
are that all assumptions and data are identified, the
dose-response model is given, and an acceptable level
of risk is specified (Nicas & Hubbard, 2003).
Expert Opinion Method
The expert opinion method is a qualitative ap-
proach to making decisions about respirators based
on the subjective professional judgment of one or
more experts. This approach has been used when
the important data needed for quantitative respira-
tor selection methods are either uncertain or un-
available. Respirator selection is made after consider-
ing the characteristics of job activities that are recog-
nized or anticipated to involve risks of exposure to
airborne contaminants; consideration of the specific
agent involved; and knowledge of the assigned pro-
tection factors, advantages, and disadvantages of vari-
ous respirators. This approach has been criticized
because, in some cases, details of the method are ill-
defined, and a rationale for the final decision is typi-
cally not provided with respirator recommendations
to explain how decisions were made (Nicas & Hub-
bard, 2003; Nicas et al., 2000).
The expert opinion method has been used to
recommend respirators for protection against expo-
sures to M. tuberculosis (Centers for Disease Control
and Prevention [CDC], 1994), Histoplasma capsula-
tum (Lenhart, Schafer, Singal, & Hajjeh, 1997), B.
anthracis (CDC, 2001, November 6), hantavirus pul-
monary syndrome (CDC, 2002), and biological
agents of bioterrorism events (CDC, 2001, October
25
25). A method using expert opinion and a modifica-
tion of the hazard ratio method was published to
address respirator selection for healthcare workers
exposed to infectious aerosols (McCullough &
Brosseau, 1999). This approach, which could be
termed a qualitative ranking method, uses qualita-
tive rankings of airborne concentrations (instead of
contaminant measurements themselves) and rank-
ings of “toxicity” or risk (as surrogates for occupa-
tional exposure limits) to identify graphically the
level of respiratory protection to which assigned pro-
tection factors could be compared.
In some applications of the expert opinion
method, categorical risk estimates are developed
with the levels of recommended respiratory protec-
tion increasing as the levels of perceived risk in-
crease. An example of an application of this ap-
proach to an infectious aerosol is the CDC guidance
document for protecting workers at risk of exposure
to H. capsulatum spores (Lenhart et al., 1997). Respi-
rators are described in that guide that should be
worn during work activities associated with expo-
sures to spore-contaminated airborne dust. The rec-
ommended respirators range from disposable, filter-
ing facepiece respirators for low-risk situations (e.g.,
site surveys of bird roosts) to full-facepiece, powered
air-purifying respirators for extremely dusty work
(e.g., removing accumulated bird or bat manure
from an enclosed area such as an attic).
Another example of an application of the expert
opinion method is the rationale used to select full-
facepiece powered air-purifying respirators for CDC
investigators performing environmental sampling for
B. anthracis in post offices and other environments
(CDC, 2001, November 6). This application differs
from the previous example in that, instead of rank-
ing respirator options according to perceived in-
creases in levels of exposure, acceptable respirators
were described as those respirators that met specific
criteria. Factors considered important in that appli-
cation of the expert opinion method included the
following:
y The infective dose (the potency) of the B. an-
thracis spores was unknown. To be conservative, the
spore-containing material in contaminated letters
was considered to have been bioengineered to make
it highly infectious. Also, no reliable estimates of
possible exposure levels were available, and it was
likely that they would have varied considerably by
location, time, and the investigators’ activities. For
these reasons, a higher level of protection than the
90 percent exposure reduction generally associated
with negative-pressure, half-facepiece respirators was
considered essential. Consequently, they were elimi-
nated from further consideration.
y Metropolitan mail processing and distribution
centers are large facilities, and the investigators do-
ing environmental sampling needed a respirator that
allowed mobility and the ability to wear the respira-
tor comfortably for an hour or more. These factors
eliminated supplied air respirators (because hose
lines limit mobility) and self-contained breathing
apparatuses (because of their limited service-life and
weight). The options remaining were air-purifying,
full-facepiece respirators and powered air-purifying
respirators with half- or full-facepieces, hoods, or
loose-fitting facepieces or helmets.
y The final step was selecting the respirator type
having the highest assigned protection factor from
the remaining options. Thus, a NIOSH-certified,
powered air-purifying respirator with a full facepiece
was selected.
Characteristics of Infectious Particles
In certain situations, healthcare workers have
risks of exposure to infectious aerosols that may re-
sult in the transmission of infection. Infection con-
trol precautions to prevent this method of agent
transmission have been termed airborne precautions
(Garner & Hospital Infection Control Practices Ad-
visory Committee, 1996). Precautions for preventing
the spread of infectious disease agents by other
routes of exposure include contact precautions (to
prevent spread by direct and indirect contact) and
droplet precautions (to prevent spread associated
with deposition of projected droplets, splatter, and
sprays onto conjunctivae, nasal mucosa, and the
mouth) (Garner & Hospital Infection Control Prac-
tices Advisory Committee, 1996).
Risks of person-to-person transmission of infec-
tious aerosols in healthcare settings have been associ-
ated with actions such as speaking, sneezing, or
spontaneous coughing by patients with contagious
Lenhart / Seitz / Trout / Bollinger
26
Issues Affecting Respirator Selection for Workers Exposed to Infectious Aerosols
respiratory infections. Person-to-person transmission
is also associated with cough-inducing or aerosol-
generating procedures such as aerosolized medica-
tion administration, diagnostic sputum induction,
bronchoscopy, airway suctioning, and endotracheal
intubation performed on patients. In some cases,
spread of an infectious agent may occur indirectly
from handling contaminated fomites (e.g., smallpox
virus transmission from handling infected bed linens
and clothing contaminated with scabs and vesicle
fluid from skin lesions [Downie et al., 1965; Tho-
mas, 1974]). Methods of protecting healthcare work-
ers from airborne transmission of infectious agents
include engineering and administrative controls,
respirators, disease prevention interventions such as
active immunization or antibiotic prophylaxis, or
combinations of these measures.
Size Distributions of Particles in Aerosols
from Possibly Infectious Persons
The factors influencing whether an infectious
agent will be transmitted by airborne spread to an-
other person include the size of the particles pro-
duced by contagious persons, the airborne concen-
trations and inhalational dose of the microorganism,
characteristics of the microorganism (e.g., infectivity,
pathogenicity, and viability after exposure to envi-
ronmental stresses), environmental factors (e.g., air
movement, temperature, relative humidity, and
sunlight), and host factors (e.g., susceptibility and
immunization status) (Cole & Cook, 1998; McCul-
lough & Brosseau, 1999). Of these factors, one that
has received particular attention relating to the selec-
tion of respirators for healthcare workers concerns
the sizes of the particles comprising an infectious
aerosol.
Conflicting meanings applied to the term
“droplet” are central to the issue of particle sizes pro-
duced by persons with contagious respiratory infec-
tions and are a source of continuing confusion. For
example, OSHA addressed issues related to infec-
tious aerosols, droplets, and the role of surgical
masks in protecting healthcare workers in the pream-
ble of its bloodborne pathogens standard, Title 29
CFR 1910.1030 (OSHA, 1991). Regarding infec-
tious aerosols and whether a potential for airborne
transmission existed, OSHA wrote that conflicting
opinions and a lack of information prevented it
from forming an opinion on the matter, and conse-
quently, the agency did not believe it was justified in
pursuing regulation of aerosols.
Regarding protection against exposure to drop-
lets, the OSHA bloodborne pathogens standard re-
quires that masks in combination with eye protec-
tion devices, such as goggles or glasses with solid side
shields, or chin-length face shields, shall be worn
whenever splashes, spray, spatter, or droplets of
blood or other infectious materials may be gener-
ated, and eye, nose, or mouth contamination can be
reasonably anticipated. In the preamble, OSHA
clarified further that protection of mucous mem-
branes of the face and upper respiratory tract against
large-droplet spattering could be provided by glasses,
face shields, and surgical masks, alone or in combi-
nation as appropriate to the task being performed
(OSHA, 1991).
OSHA did not cite the specific sizes of droplets
against which the use of barrier precautions would
be protective. However, by stating that the blood-
borne pathogens standard did not apply to infec-
tious aerosols and by using words such as sprays,
splashes, and spatter, the agency implied that the
droplets addressed in the standard are those particles
sometimes referred to as projectile particles. Projec-
tile particles are large enough to be visible to the na-
ked eye, are essentially unaffected by room air cur-
rents, and remain airborne only briefly. They have
ballistic trajectories that do not deviate from their
courses until they collide head-on with or impact a
surface. In physiological terms, droplets created by
sprays, splashes, and spatters are distinguished from
aerosol particles in that they are much too large to
be inhaled; for this reason, they have also been
called nonrespirable particles.
The position of OSHA was that barrier devices
such as glasses, face shields, and surgical masks
would protect healthcare workers from infectious
agents generated as large-particle droplets of sprays,
splashes, or spatters. However, a conflict arises when
comparing the term “droplet” to describe particles
that settle out quickly (as used by OSHA and sum-
marized above) and the term “droplet” as used in
infection control documents. Part II of the Guideline
for Isolation Precautions in Hospitals states that the
27
OSHA bloodborne pathogens standard requires the
wearing of masks, eye protection, and face shields to
reduce the risk of exposures to bloodborne patho-
gens and that healthcare workers generally can wear
surgical masks as protection against the spread of
infectious large-particle droplets (Garner & Hospital
Infection Control Practices Advisory Committee,
1996). However, large-particle droplets were defined
in the guideline as particles larger than 5 micrometer
(m) and generated either by an infected person dur-
ing coughing, sneezing, or talking or during the per-
formance of procedures such as suctioning and bron-
choscopy. Furthermore, particles of 5 m or less
were defined as droplet nuclei (i.e., residues of
evaporated droplets [Wells, 1955]). The rationale
supporting this definition of large-particle droplets
as 5 m and larger and the view that surgical masks
protected against exposures to them are unstated
and, as will be demonstrated below, may be flawed.
Critical to this discussion is the distinction be-
tween the size of particles comprising an aerosol and
the size of particles that settle out quickly. From the
principles of aerosol physics, spherical particles set-
tling freely in still air are known to reach an equilib-
rium or terminal settling velocity. The terminal set-
tling velocity of a particle can be calculated and is a
function of the viscosity and density of air, the parti-
cle’s density and its diameter squared, and accelera-
tion due to gravity (Baron & Willeke, 2001).
The terminal settling velocities of particles can
be used to distinguish particles that tend to remain
airborne from those that settle out. For example, the
terminal settling velocity of a particle of unit density
(i.e., 1 gram per cubic centimeter) and a diameter of
100 m is approximately 30 centimeters per second
(cm/sec) (Baron & Willeke, 2001), which suggests
that particles of this size and larger will settle quickly
on surfaces near the point at which they were gener-
ated. By comparison, a particle with the same unit
density and a diameter of 5 m (which is the cut-off
used in the infection control guide) has a terminal
settling velocity of only 0.08 cm/sec (Baron &
Willeke, 2001), and thus, it tends to remain air-
borne for a relatively long time. Therefore, as a rule-
of-thumb, airborne particles having diameters of 100
m or less have been defined as comprising an aero-
sol, and those greater than 100 m are particles that
will settle out quickly (Baron & Willeke, 2001;
Hirshfeld & Laub, 1941; Wells, 1934). Conse-
quently, an assumption that all droplets greater than
5m are large-particle droplets that do not remain
suspended in the air and generally travel only short
distances, usually 3 feet or less, through the air
(Garner & Hospital Infection Control Practices Ad-
visory Committee, 1996) is inconsistent with well-
established understanding of how aerosol particles
behave.
Duguid (1946) and Papineni & Rosenthal
(1997) studied the sizes of droplets expelled during
talking, coughing, sneezing, nose breathing, and
mouth breathing. Duguid used a microscope to esti-
mate the size of respiratory droplets by measuring
stain marks on slides exposed directly to mouth
spray. He reported that droplets produced by talk-
ing, coughing, and sneezing ranged from 1 to 2,000
m; 95% of the droplets had diameters between 2
and 100 m; and most droplets had diameters be-
tween 4 and 8 m (Duguid, 1946). The composition
and bacterial or viral content of droplets and droplet
nuclei are likely to be highly variable, with large ag-
gregate droplets and strings of mucus possibly con-
taining many organisms and droplet nuclei contain-
ing one or two organisms at most and sometimes
containing none (Reponen, Willeke, & Nevalainen,
2001; Riley & O’Grady, 1961; Wells, 1955).
More recently, Papineni and Rosenthal (1997)
used an optical particle counter and transmission
electron microscope to characterize the size distribu-
tion of droplets exhaled by mouth breathing, nose
breathing, coughing, and talking. They reported that
the diameters of respiratory droplets produced by
healthy persons ranged from 0.3 m (the lower limit
of detection of the sampling method) to approxi-
mately 8 m. The findings of a study comparing the
elimination of inhaled 6-m Teflon particles from
the tracheobronchial tract of healthy persons and
patients with respiratory tract disease showed that
only patients with increased respiratory secretions
eliminated test particles from their lungs by cough-
ing (Camner, Mossberg, Philipson, & Strandberg,
1979). Thus, a conclusion was made that increased
respiratory secretions were necessary for coughing to
be an effective means of eliminating particles. In-
creased secretion of fluids on airway surfaces and
Lenhart / Seitz / Trout / Bollinger
28
Issues Affecting Respirator Selection for Workers Exposed to Infectious Aerosols
greater respiratory actions such as coughing and
sneezing by persons with respiratory illnesses may
alter the size distribution of their exhaled droplets
and increase droplet concentrations (Papineni &
Rosenthal, 1997).
Droplets Versus Droplet Nuclei
If expelled droplets remained at their original
size, those having diameters greater than 100 m
would settle rapidly from the air, and only people
close to an infectious patient would be at risk for
exposure to these large aerosolized particles (Burge,
1995; Silverman, Billings, & First, 1971; Wells,
1934). However, droplets do not remain the same
size after being expelled, but rather they begin imme-
diately to evaporate and within seconds, or even frac-
tions of a second, become droplet nuclei (Burge,
1995; Silverman et al., 1971; Wells, 1934).
From a size distribution of the droplets emitted
during sneezing, one researcher concluded that prac-
tically all droplets would rapidly evaporate to droplet
nuclei (Riley & O’Grady, 1961). To demonstrate
how rapidly droplets evaporate, Wells (1955) calcu-
lated the drying times (total evaporation times) of
water droplets having diameters of 100 and 50 m
falling in unsaturated (50% relative humidity) air
and reported times of 1.3 and 0.3 second, respec-
tively. More recently, Ferron and Soderholm (1990)
calculated the drying time of a water droplet having
a diameter of 50 m in 50% relative humidity air to
be approximately 5 seconds. Despite this latter esti-
mate being more conservative than that of Wells, the
results still demonstrate that small water droplets
evaporate quickly; that is, water droplets having di-
ameters of 20 m and smaller were calculated to
evaporate in less than 1 second (Ferron & Soder-
holm, 1990). Wells, and Ferron and Soderholm
based their calculations on pure water particles.
Droplets containing dissolved substances, such as
salts and proteins, or containing a microorganism
would likely evaporate less rapidly than a water drop-
let (Riley & O’Grady, 1961).
Duguid (1946) measured the size of droplet nu-
clei collected on oiled slides exposed in a slit sampler
and reported that their diameters ranged from 0.25
to 42 m; 97% of the droplet nuclei were between
0.5 and 12 m; and most droplet nuclei had diame-
ters between 1 and 2 m. Duguid’s findings demon-
strated also that the most common expired droplets
were between 4 and 8 m, and therefore, for practi-
cal purposes, are so small that they may be consid-
ered to behave in air like droplet nuclei. Particles in
these size ranges and larger are affected by turbulent
air movement created by worker activities and the
ventilation in a room. The result is that aerosolized
particles smaller than 100 m can remain suspended
in air for prolonged periods of time because typical
room air velocities (10 to 30 cm/sec [Baldwin &
Maynard, 1998; Silverman et al., 1971]) exceed the
terminal settling velocities of the particles.
Applications Concerning Characteristics
of Infectious Aerosols
Recommendations for isolation precautions in
hospitals have defined the sizes of large-particle
droplets as greater than 5 m and the sizes of
droplet nuclei as 5 m or less (Garner & Hospital
Infection Control Practices Advisory Committee,
1996). Whether a healthcare worker is judged to be
exposed to infectious droplets or infectious droplet
nuclei have been controversial and are at the heart
of some debates concerning the level of protection
needed by healthcare workers exposed to infectious
agents. Among the subjects of these debates are two
high-priority infectious disease agents posing a risk
to national security—variola (smallpox) virus and
Yersina pestis (plague) bacteria (CDC, 2000). Because
a terrorist attack involving smallpox or plague is
likely to involve covert dissemination, healthcare
workers would likely be the first to identify exposed
individuals when they became ill. These workers
would be at risk for infection by person-to-person
transmission.
Person-to-person spread of pneumonic plague is
known to occur, and although very uncommon in
the United States, bioterrorism preparedness has
made this a topic of concern (Inglesby et al., 2000).
Guidelines addressing infection control for pneu-
monic plague state that there is no epidemiological
evidence suggesting person-to-person spread of pneu-
monic plague by droplet nuclei and that the
mechanism of transmission is via respiratory drop-
lets at close contact, within 6 feet (Garner & Hospi-
tal Infection Control Practices Advisory Committee,
29
1996; Inglesby et al., 2000; Inglesby, Henderson,
O’Toole, & Dennis, 2000). Because of this, some
researchers consider surgical masks sufficient for pro-
tecting healthcare workers from person-to-person
transmission of pneumonic plague and wearing a
respirator to be unwarranted. However, Y. pestis has
been found in oral secretions of infected animals
and humans (Chernin, 1989; Meyer, 1961; Speck &
Wolochow, 1957). As reviewed above, aerosols from
infected patients can, in the course of routine activi-
ties and procedures, produce small particles that will
remain airborne for long periods. In fact, some have
argued that the possibility of transmission of pneu-
monic plague by droplet nuclei should not be dis-
missed and have recommended that healthcare
workers at risk should wear a respirator (Hawley &
Eitzen, 2001; Levison, 2000).
Regarding smallpox, guidelines have stated that
the smallpox virus is transmitted predominantly by
droplets during close contact with an infectious per-
son. CDC has defined close contact as being within
6 to 7 feet of a smallpox patient (CDC, 2003). How-
ever, the findings in one experimental study have
shown that sedimentation plates placed 20 feet from
the bed of a smallpox patient were positive for vari-
ola virus (Thomas, 1974), and epidemiological evi-
dence (i.e., the findings of an outbreak investigation)
suggested that droplet-nuclei transmission was re-
sponsible for causing a smallpox outbreak in a Ger-
man hospital (Wehrle, Posch, Richter, & Hender-
son, 1970). These data suggested that smallpox virus
can be transmitted via an aerosol and are in part the
basis for recommendations that healthcare workers
should wear a respirator when caring for patients
with smallpox (Association for Professionals in Infec-
tion Control and Epidemiology, 1999; CDC, 2003).
Surgical Masks Versus Respirators
Despite confusion over what particle size distin-
guishes large-particle droplets from aerosol particles,
it may be reasonable to assume that a surgical mask
might provide an adequate barrier to large-particle
droplets. However, research has shown that surgical
masks should not be depended upon to protect
healthcare workers from infectious aerosols.
The original purpose of a surgical mask was to
prevent wound contamination by bacteria from the
mouth and upper respiratory tract of surgeons. Sur-
gical masks have also been recommended for pa-
tients who are suspected of having or known to have
infectious tuberculosis as a component of routine
infection control practice (CDC, 1994). A 1941
study evaluating surgical masks made of either gauze
or muslin concluded that they were inadequate for
protecting wounds because bacteria-containing parti-
cles passed through the filter material and around
the edges of the masks (Hirshfeld & Laube, 1941).
Subsequent studies, in which not only surgical
masks made of gauze and muslin but also ones made
of paper, foam, and synthetic materials were evalu-
ated, resulted in filter efficiencies ranging from the
teens to nearly 100% (Brosseau, McCullough, &
Vesley, 1997; Ford & Peterson, 1963; Ford, Peter-
son, & Mitchell, 1967; Miller, 1973, 1995; Rogers,
1980). The findings of other studies in which surgi-
cal masks were evaluated (with some reported to
have highly efficient filters) have emphasized that a
secure face seal is essential for preventing infectious
particles from escaping (as well as entering) at a
mask’s edges (Ha’eri & Wiley, 1980; Johnson, Mar-
tin, & Resnick, 1994; Pippin, Verderame, & Weber,
1987; Tuomi, 1985).
Researchers, who have studied the aerosols and
spatters produced during some dental procedures
and the blood aerosols and spatters generated during
surgeries, defined the size of spatter droplets to be
50 m and larger (Heinsohn & Jewett, 1993; Miller,
1973). However, research has been conducted to
measure the blood-containing particles generated by
common powered dental instruments and to evalu-
ate the effectiveness of surgical masks in protecting
against exposures to these particles (Miller, 1995).
The findings of the study showed that powered den-
tal instruments aerosolized mostly respirable-sized
particles smaller than 10 m in diameter, and the
efficiencies of the tested surgical masks ranged from
17% to 85%. From these findings, Miller (1995)
concluded that “the use of surgical masks for preven-
tion of occupational infection appears to be poorly
founded” (p. 675).
A draft guidance document of the U.S. Food
and Drug Administration (FDA) describes four labo-
ratory tests for measuring the filtration efficiencies
Lenhart / Seitz / Trout / Bollinger
30
Issues Affecting Respirator Selection for Workers Exposed to Infectious Aerosols
of surgical masks (Food and Drug Administration,
2003). In lieu of providing the results of one of these
tests to the FDA, the draft proposes that mask
manufacturers can submit the NIOSH certification
number of a model of surgical mask that has been
tested and certified by NIOSH as an N95 respirator.
However, the filtration efficiency tests recommended
by FDA should not be assumed to produce results
that are equivalent to the NIOSH certification tests
of an N95 respirator.
The results of a study comparing the abilities of
a surgical mask and a NIOSH-approved N95 respira-
tor to protect workers against exposures to airborne
latex allergenic particles provide evidence suggesting
that the FDA tests might overestimate the filter effi-
ciencies of surgical masks (Mitakakis et al., 2002).
Latex exposures of 20 healthcare workers were esti-
mated using nasal air samplers (Graham, Pavlicek,
Sercombe, Xavier, & Tovey, 2000) and Institute of
Occupational Medicine filter samplers (Mark & Vin-
cent, 1986). All samples were analyzed for particles
bearing the Hev b 5 latex allergen. The results of the
study showed that wearing a mask did not signifi-
cantly reduce the number of allergenic particles in-
haled and that wearing a respirator reduced the
number of inhaled particles by 17-fold. The mask
and the respirator were made by the same manufac-
turer and appeared to be identical; however, their
filter materials were different. The particle filtration
efficiencies and bacterial filtration efficiencies of the
mask and the respirator were both reported to be
greater than or equal to 99%, but their differential
pressures differed: less than 2.0 millimeters of water
per square centimeter (mm H2O/cm2) for the mask
and less than 5.0 mm H2O/cm2 for the respirator
(Shalfoon Dental Limited, 2002a, 2002b). Because
the mask and respirator had the same facepiece fit-
ting characteristics, the most likely explanation for
the difference in the levels of protection provided
between the mask and the respirator was penetration
of particles through the mask’s filter material rather
than face seal leakage (C. Solano, Kimberly-Clark
Corporation, N. Richland Hills, TX, personal com-
munication, September 3, 2003).
Conclusions and Recommendations
Air concentration measurements and exposure
limits applicable to infectious disease agents to
which workers may be exposed are essentially non-
existent, and the absence of these essential data im-
pedes the process of selecting appropriate respiratory
protection. Until particle-size distributions and the
viability and infectivity of particles comprising infec-
tious aerosols generated in healthcare settings can be
better characterized, the expert opinion method will
likely continue as the method used most frequently
to make respirator selections for healthcare workers.
Specifying the rationale and all data inputs used in a
respirator selection process is essential when using
this method. Important factors to consider include
the known limitations of data, historical experience
with infectious agents in epidemiological evaluations
of outbreak situations, availability of information on
infectious diseases, work tasks perceived to result in
potentially higher risk for aerosol exposure, and the
known properties of and experience with respirators
in healthcare settings and other workplaces.
Outbreaks of new and emerging infectious dis-
eases may present the most difficult challenges to the
selection and use of respirators in healthcare settings
where workers’ risks of exposure to an infectious
agent (e.g., the etiology of the problem, the source or
mode of transmission) are uncertain (Goodman,
Buehler, & Koplan, 1990; Reingold, 1998). Health-
care workers caring for patients in such settings may
be at risk of infection while the data of the outbreak
investigation are being collected and analyzed. The
importance of balancing the need for thorough as-
sessment of causality with the potentially conflicting
need to intervene quickly to protect the health of
workers means, in practice, that implementing con-
trol measures will oftentimes be appropriate at any
point in the outbreak investigation sequence
(Reingold, 1998). This public health approach is
consistent with guidance concerning occupational
health practice that states: “When doubts exist about
the severity of an occupational hazard, prudent pre-
cautionary action must be considered immediately
and taken as appropriate” (International Commis-
sion on Occupational Health, 2002).
31
Lenhart / Seitz / Trout / Bollinger
In response to outbreaks of new or emerging
infectious diseases, administrators of respirator pro-
grams should use all available data to make respira-
tor selection decisions. Whenever possible, data col-
lected during an outbreak investigation should
include descriptions of respirators (e.g., manufac-
turer, model number, NIOSH certification number)
worn by healthcare workers when caring for infec-
tious patients; whether respirators with tight-fitting
facepieces were assigned based on facepiece fit-
testing; whether respirators were worn correctly; the
nature of ventilation conditions in patients’ rooms
(e.g., ventilation effectiveness, air change rates); and
estimates of the air concentration, size, and infectiv-
ity of infectious particles generated by a patient or an
aerosol-generating procedure.
In cases where doubt remains about the level of
protection that should be recommended, a respira-
tor type having a higher assigned protection factor
can be selected until additional data are gathered
indicating that protection could be provided by a
respirator having a lower assigned protection factor
or even that respirator use could safely be stopped
entirely. (This approach was used in healthcare set-
tings during the 2003 outbreak of severe acute respi-
ratory syndrome [Twu et al., 2003]). Increased mone-
tary costs of maintaining a respirator program is a
factor to consider with this conservative approach.
Other potential factors to consider in healthcare set-
tings using this approach could include conse-
quences related to infection control (i.e., increased
potential for contact contamination) and interfer-
ence with patient care.
Evidence is presented in this paper supporting a
position that 100 m, and not 5 m, should be con-
sidered the particle size defining the boundary be-
tween large-particle droplets and aerosol particles.
Information is also presented demonstrating that,
although healthcare workers caring for patients with
contagious respiratory infections are at risk of expo-
sure to large-particle droplets greater than 100 m in
diameter, their risks of inhalational exposure to in-
fectious particles are likely to be predominantly to
an aerosol consisting of a mixture of rapidly evapo-
rating droplets and droplet nuclei that remain sus-
pended in room air for prolonged periods of time.
Applications of polymerase chain reaction-based
methods for analyzing air samples collected in
healthcare settings have shown promise for provid-
ing insight to the nosocomial spread of viral patho-
gens (Aintablain, Walpita, & Sawyer, 1998; Sawyer,
Chamberlin, Wu, Aintablain, & Wallace, 1994). For
example, contact with contaminated secretions and
large-particle droplets are thought to be the primary
route of transmission of both respiratory syncytial
virus and Bordetella pertussis. However, the possibility
that aerosol particles may contribute to the nosoco-
mial transmission of these agents has been suggested
by the detection of their nucleic acid material in air
at relatively large distances from patients’ beds
(Aintablain et al., 1998). Whether the quantities
detected are sufficient to transmit an infectious dose
or whether the material detected represents viable,
infectious organisms is unknown. These findings
suggest that defining a specific distance as the
boundary of a healthcare worker’s exposure to parti-
cles expired by a patient with a contagious respira-
tory infection may be inappropriate.
Dependence on the findings of outbreak investi-
gations to suggest indirectly whether large-particle
droplets (in which case wearing a surgical mask
would be indicated) or droplet nuclei (in which case
wearing a respirator would be indicated) are respon-
sible for transmission of an infectious agent does not
sufficiently account for other important characteris-
tics of infectious aerosols. Thus, when making a res-
pirator selection, factors in addition to the findings
of outbreak investigations and data concerning the
size distribution of the airborne infectious particles
are likely to be important. These other factors in-
clude estimates of the air concentrations of infec-
tious particles generated by different activities, esti-
mates of the amount of time that a healthcare
worker will be near an infectious patient or to proce-
dures likely to generate infectious aerosols, and the
characteristics of the infectious agent (e.g., its infec-
tivity and viability after exposure to evaporation and
other environmental stresses).
A finding that the highest air concentrations of
viable, respirable-size infectious particles most likely
occur during aerosol-generating procedures could
lead to a recommendation that respirators that pro-
vide higher levels of protection should be used by
nearby healthcare workers (Singh et al., 2003). For
32
Issues Affecting Respirator Selection for Workers Exposed to Infectious Aerosols
example, use of a powered air-purifying respirator
was recommended instead of a negative-pressure air-
purifying respirator for situations where healthcare
workers were likely to encounter high levels of infec-
tious aerosols during autopsy, orthopedic proce-
dures, and bronchoscopy (Johnson et al., 1994). The
rationale of this selection included the following
advantages of this respirator: face-seal leakage is es-
sentially prevented by the device’s air flow rate; the
presence of a face shield; and the ability to protect
people with beards. Similarly, wearing a powered
air-purifying respirator has been recommended for
healthcare workers during cough-inducing proce-
dures on patients suspected of having tuberculosis
or during autopsies on deceased persons suspected
of having had tuberculosis (Fennelly, 1997, 1998;
Fennelly & Nardell, 1998; McCullough & Brosseau,
1999; Nicas, 1995).
The filter media of surgical masks allow penetra-
tion of small particles, and the poor fitting character-
istics of their face seals allow the passage of particles
at the edges of the masks. Thus, only NIOSH-
certified respirators should be used as part of a strat-
egy for protecting workers from inhalational expo-
sures to infectious aerosols. Surgical masks may be
useful as barrier devices for protecting the mucous
membranes of a worker’s nose and mouth from in-
advertent exposures in situations where the only risk
is to large-particle droplets of splashes, sprays, or
spatters of blood or other potentially infectious ma-
terial (Mangram et al., 1999). However, surgical
masks cannot be considered respirators.
Finally, preventing the inhalational transmission
of infectious disease agents remains only one compo-
nent of infection control. Other mechanisms of in-
fectious agent transmission must also be addressed
comprehensively by the application of contact pre-
cautions and other preventive measures.
Acknowledgement
The authors gratefully acknowledge the always
outstanding editorial work of Ms. Priscilla Wopat of
the Spokane Research Laboratory of the National
Institute for Occupational Safety and Health.
References
Aintablain, N., Walpita, P., & Sawyer, M. H. (1998).
Detection of Bordetella pertussis and respiratory
syncytial virus in air samples from hospital rooms.
Infection Control and Hospital Epidemiology, 19, 918-923.
American National Standards Institute. (1992).
American national standard for respiratory protection
(ANSI Z88.2-1992). New York: American National
Standards Institute.
Association for Professionals in Infection Control
and Epidemiology. (1999, April 13). Bioterrorism
readiness plan: A template for healthcare facilities.
Retrieved January 1, 2004, from www.cdc.gov/
ncidod/hip/Bio/13apr99APIC-CDCBioterrorism.
PDF.
Baldwin, P. E. J., & Maynard, A. D. (1998). A survey
of wind speeds in indoor workplaces. Annals of Occu-
pational Hygiene, 42, 303-313.
Baron, P. A., & Willeke, K. (Eds.). (2001). Aerosol
measurement principles, techniques, & applications (2nd
ed.). New York: John Wiley and Sons, Inc.
Brosseau, L. M., McCullough, N. V., & Vesley, D.
(1997). Mycobacterial aerosol collection efficiency of
respirator and surgical mask filters under varying
conditions of flow and humidity. Applied Occupa-
tional and Environmental Hygiene, 12, 435-445.
Burge, H. A. (1995). Airborne contagious disease. In
H. A. Burge (Ed.), Bioaerosols. Boca Raton, FL: Lewis
Publishers.
Camner, P., Mossberg, B., Philipson, K., &
Strandberg, K. (1979). Elimination of test particles
from the human tracheobronchial tract by voluntary
coughing. Scandinavian Journal of Respiratory Diseases,
60, 56-62.
Centers for Disease Control and Prevention.
(October 28, 1994). Guidelines for preventing the
transmission of Mycobacterium tuberculosis in
health-care facilities, 1994. Morbidity and Mortality
33
Lenhart / Seitz / Trout / Bollinger
Weekly Report, 43(RR13), 1-132. Retrieved January 1,
2004 from www.c d c . g o v/mmwr/pre v i ew/
mmwrhtml/00035909.htm.
Centers for Disease Control and Prevention. (2000).
Biological and chemical terrorism: Strategic plan
for preparedness and response. Morbidity and Mortal-
ity Weekly Report, 49(RR04), 1-14.
Centers for Disease Control and Prevention. (2001,
October 25). Interim recommendations for the selec-
tion and use of protective clothing and respirators
against biological agents. Retrieved January 1, 2004,
from www.bt.cdc.gov/documentsapp/Anthrax/
Protective/10242001Protect.asp.
Centers for Disease Control and Prevention. (2001,
November 6). Protecting investigators performing
environmental sampling for Bacillus anthracis: Per-
sonal protective equipment. Retrieved January 1,
2004, from www.bt.cdc.gov/DocumentsApp/
Anthrax/Protective/protective.asp.
Centers for Disease Control and Prevention. (July
26, 2002). Hantavirus pulmonary syndrome B
United States: Updated recommendations for risk
reduction. Morbidity and Mortality Weekly Report,
51(RR09), 1-12. Retrieved January 1, 2004, from
www.cdc.gov/mmwr/preview/mmwrhtml/rr5109a1.
htm.
Centers for Disease Control and Prevention (2003,
October 28). Smallpox response plan and guidelines
(version 3.0). Retrieved January 1, 2004, from
www.bt.cdc.gov/agent/smallpox/response-plan/
index.asp.
Chernin, E. (1989). R. P. Strong and the Manchurian
epidemic of pneumonic plague, 1910-1911. Journal of
the History of Medicine and Allied Sciences, 44, 296-319.
Cole, E. C., & Cook, C. E. (1998). Characterization
of infectious aerosols in healthcare facilities: An aid
to effective engineering controls and preventive
strategies. American Journal of Infection Control, 26,
453-464.
Downie, A. W., Meiklejohn, M., St. Vincent, L.,
Rao, A. R., Sundara Babu, B. V., & Kempe, C. H.
(1965). The recovery of smallpox virus from patients
and their environment in a smallpox hospital. Bulle-
tin of the World Health Organization, 33, 615-622.
Duguid, J. P. (1946). The size and the duration of
air-carriage of respiratory droplets and droplet-
nuclei. Journal of Hygiene, 44, 471-479.
Fennelly, K. P. (1997). Personal respiratory protec-
tion against Mycobacterium tuberculosis.Clinics in Chest
Medicine, 18, 1-17.
Fennelly, K. P. (1998). The role of masks in prevent-
ing nosocomial transmission of tuberculosis. Interna-
tional Journal of Tuberculosis and Lung Disease, 2(9
Suppl 1), S103-S109.
Fennelly, K. P., & Nardell, E. A. (1998). The relative
efficacy of respirators and room ventilation in pre-
venting occupational tuberculosis. Infection Control
and Hospital Epidemiology, 19, 754-759.
Ferron, G. A., & Soderholm, S. C. (1990). Estima-
tion of the times for evaporation of pure water drop-
lets and for stabilization of salt solution particles.
Journal of Aerosol Science, 21, 415-429.
Food and Drug Administration. (2003, May 15).
Surgical masks—premarket notification [510(k)] sub-
missions; draft guidance for industry and FDA. Re-
trieved January 1, 2004, from www.fda.gov/cdrh/
ode/guidance/094.html.
Ford, C. R., & Peterson, D. E. (1963). The efficiency
of surgical masks. American Journal of Surgery, 106,
954-957.
Ford, C. R., Peterson, D. E., & Mitchell, C. R.
(1967). An appraisal of the role of surgical face
masks. American Journal of Surgery, 113, 787-790.
Garner, J. S., & Hospital Infection Control Practices
Advisory Committee. (1996). Guideline for isolation
precautions in hospitals: Parts I and II. Infection Con-
trol and Hospital Epidemiology, 17, 53-80, and Ameri-
34
Issues Affecting Respirator Selection for Workers Exposed to Infectious Aerosols
can Journal of Infection Control, 24, 24-52. Retrieved
January 1, 2004, from www.cdc.gov/ncidod/hip/
isolat/isolat.htm.
Goodman, R. A., Buehler, J. W., & Koplan, J. P.
(1990). The epidemiologic field investigation: Sci-
ence and judgment in public health practice. Ameri-
can Journal of Epidemiology, 132, 9-16.
Graham, J. A., Pavlicek, P. K., Sercombe, J. K., Xavier,
M. L., & Tovey, E. R. (2000). The nasal air sampler:
A device for sampling inhaled aeroallergens. Annals of
Allergy, Asthma, and Immunology, 84, 599-604.
Guy, H. P. (1985). Respirator performance terminol-
ogy. American Industrial Hygiene Association Journal,
46, B22 and B24.
Ha’eri, G. B., & Wiley, A. M. (1980). The efficiency
of standard surgical face masks: An investigation
using “tracer particles.” Clinical Orthopaedics and Re-
lated Research, 148, 160-162.
Hawley, R. J., & Eitzen, E. M. (2001). Biological
weapons—a primer for microbiologists. Annual Re-
view of Microbiology, 55, 235-253.
Heinsohn, P., & Jewett, D. L. (1993). Exposure to
blood-containing aerosols in the operating room: A
preliminary study. American Industrial Hygiene Associa-
tion Journal, 54, 446-453.
Hirshfeld, J. W., & Laube, P. J. (1941). Surgical
masks: An experimental study. Surgery, 9, 720-730.
Inglesby, T. V., Dennis, D. T., Henderson, D. A., et
al. (2000). Plague as a biological weapon--medical
and public health management. Journal of the Ameri-
can Medical Association, 283, 2281-2290.
Inglesby, T. V., Henderson, D. A., O’Toole, T., &
Dennis, D. T. (2000). Safety precautions to limit
exposure from plague-infected patients—in reply.
Journal of the American Medical Association, 284, 1649.
International Commission on Occupational Health
(2002). International code of ethics for occupational
health professionals. Retrieved January 1, 2004, from
www.icoh.org.sg/eng/core/code_ethics_eng.pdf.
Johnson, B., Martin, D. D., & Resnick, I. G. (1994).
Efficacy of selected respiratory protective equipment
challenged with Bacillus subtilis subsp. niger.Applied
Environmental Microbiology, 60, 2184-2186.
Johnston, A. R. (2001). Introduction to selection
and use. In C. E. Colton & L. M. Brosseau (Eds.),
Respiratory protection, a manual and guideline (3rd ed.)
(pp. 13-24). Fairfax, VA: AIHA Press.
Lenhart, S. W., Schafer, M. P., Singal, M., & Hajjeh,
R. A. (1997). Histoplasmosis: Protecting workers at risk.
U.S. Department of Health and Human Services,
Public Health Service, Centers for Disease Control
and Prevention, National Institute for Occupational
Safety and Health, DHHS (NIOSH) Publication No.
97-146. Retrieved January 1, 2004, from www.cdc.
gov/niosh/97 146.html.
Levison, M. E. (2000). Safety precautions to limit
exposure from plague-infected patients. Journal of the
American Medical Association, 284, 1648.
Mangram, A. J., Horan, T. C., Pearson, M. L., Silver,
L. C., Jarvis, W. R., & Hospital Infection Control
Practices Advisory Committee. (1999). Guideline for
prevention of surgical site infection, 1999. Infection
Control and Hospital Epidemiology, 20, 250-278.
Mark, D., & Vincent, J. H. (1986). A new personal
sampler for airborne total dust in workplaces. Annals
of Occupational Hygiene, 30, 89-102.
McCullough, N. V., & Brosseau, L. M. (1999). Se-
lecting respirators for control of worker exposure to
infectious aerosols. Infection Control and Hospital Epi-
demiology, 20, 136-144.
Meyer, K. F. (1961). Pneumonic plague. Bacteriologi-
cal Review, 25, 249-261.
Miller, R. L. (1973). Studies of the aerobiology of
dentistry. In J. F. Hers & K. C. Winkler (Eds.), Air-
borne transmission and airborne infection, concepts and
35
Lenhart / Seitz / Trout / Bollinger
methods presented at the sixth international symposium on
aerobiology. New York: John Wiley and Sons, Inc.
Miller, R. L. (1995). Characteristics of blood-
containing aerosols generated by common powered
dental instruments. American Industrial Hygiene Asso-
ciation Journal, 56, 670-676.
Mitakakis, T. Z., Tovey, E. R., Yates, D. H., Toelle,
B. G., Johnson, A., Sutherland, M. F., et al. (2002).
Particulate masks and non-powdered gloves reduce
latex allergen inhaled by healthcare workers. Clinical
and Experimental Allergy, 32, 1166-1169.
Myers, W. R., Lenhart, S. W., Campbell, D., & Pro-
vost, G. (1983). Letter to the Editor (topic: Respira-
tor performance terminology). American Industrial
Hygiene Association Journal, 44, B25-B26.
National Institute for Occupational Safety and
Health. (1987). Respirator decision logic. Cincinnati,
OH: U.S. Department of Health and Human Ser-
vices, Public Health Service, Centers for Disease
Control, National Institute for Occupational Safety
and Health, DHHS (NIOSH) Publication No. 87-
108. Retrieved January 1, 2004, from www.cdc.gov/
niosh/87 108.html.
Nicas, M. (1995). Respiratory protection and the risk
of Mycobacterium tuberculosis infection. American Jour-
nal of Industrial Medicine, 27, 317-333.
Nicas, M. (1996). Refining a risk model for occupa-
tional tuberculosis transmission. American Industrial
Hygiene Association Journal, 57, 16-22.
Nicas, M., & Hubbard, A. (2002). A risk analysis for
airborne pathogens with low infectious doses: Appli-
cation to respirator selection against Coccidioides im-
mitis spores. Risk Analysis, 22, 1153-1163.
Nicas, M., & Hubbard, A. (2003). A risk analysis
approach to selecting respiratory protection against
airborne pathogens used for bioterrorism. American
Industrial Hygiene Association Journal, 64, 95-101.
Nicas, M., Neuhaus, J., & Spear, R. C. (2000). Risk-
based selection of respirators against infectious aero-
sols: Application to anthrax spores. Journal of Occupa-
tional and Environmental Medicine, 42, 737-748.
Occupational Safety and Health Administration.
(December 6, 1991). Preamble to the OSHA Blood-
borne Pathogens Standard (29 CFR 1910.1030),
Section 9, Part IX. Summary and Explanation of the
Standard. Retrieved January 1, 2004, from www.
osha.gov/pls/oshaWeb/owadisp.show_document?
p_table=PREAMBLES&p_id=811&p_text_version=
FALSE.
Occupational Safety and Health Administration.
(1998a). Preamble to the OSHA Respiratory Protec-
tion Standard (29 CFR 1910.134), Section 6, Part
VII. Summary and Explanation. Federal Register
63(5):1198-1200. Retrieved January 1, 2004 from
www.osha.gov/pls/oshaWeb/owadisp.show_docume
nt?p_table=PREAMBLES&p_id=1053&p_text_versi
on=FALSE.
Occupational Safety and Health Administration.
(1998b). Respiratory Protection Standard (29 CFR
1910.134). Washington, DC: U.S. Government
Printing Office, Office of the Federal Register.
Occupational Safety and Health Administration.
(June 6, 2003). Assigned protection factors; pro-
posed rule. Federal Register, 68(109), p. 34114.
Papineni, R. S., & Rosenthal, F. S. (1997). The size
of droplets in the exhaled breath of healthy human
subjects. Journal of Aerosol Medicine, 10, 105-116.
Pippin, D. J., Verderame, R. A., & Weber, K. K.
(1987). Efficacy of face masks in preventing inhala-
tion of airborne contaminants. Journal of Oral and
Maxillofacial Surgery, 45, 319-323.
Reingold, A. L. (1998). Outbreak investigations—A
perspective. Emerging Infectious Diseases, 4, 21-27. Re-
trieved January 1, 2004, from www.cdc.gov/ncidod/
eid/vol4no1/reingold.htm.
36
Issues Affecting Respirator Selection for Workers Exposed to Infectious Aerosols
Reponen, T., Willeke, K., & Nevalainen, A. (2001).
Biological particle sampling. In P. A. Baron & K.
Willeke (Eds.), Aerosol measurement principles, tech-
niques, & applications (2nd ed.) (p. 752). New York:
John Wiley and Sons, Inc.
Riley, R. L., & O’Grady, F. (1961). Airborne infection.
New York: The Macmillan Company.
Rogers, K. B. (1980). An investigation into the effi-
ciency of disposable face masks. Journal of Clinical
Pathology, 33, 1086-1091.
Sawyer, M. H., Chamberlin, C. J., Wu, Y. N., Ain-
tablain, N., & Wallace, M. R. (1994). Detection of
varicella-zoster virus DNA in air samples from hospi-
tal rooms. Journal of Infectious Diseases, 169, 91-94.
Shalfoon Dental Limited. (2002a, September 23).
Kimberly-Clark General Purpose Face Masks. Re-
trieved January 1, 2004, from www.shalfoon.co.nz/
Web/TechPprs.nsf/7950062053b1bb4fca256a8e00
7e4 13e/c2f84404591e 25dfc a256c3e0019 0b6b
!OpenDocument.
Shalfoon Dental Limited. (2002b, September 23).
Kimberly-Clark Particulate Filter Respirator Masks.
Retrieved January 1, 2004, from www.shalfoon.
co.nz/Web/TechPprs.nsf/7950062053b1bb4fca256
a8e007e413e/351a9a9ea15f491aca256c3e001d63e9
!OpenDocument.
Silverman, L., Billings, C. E., & First, M. W. (1971).
Particle size analysis in industrial hygiene. New York:
Academic Press.
Singh, K., Hsu, L. Y., Villacian, J. S., Habib, A.,
Fisher, D., & Tambyah, P. A. (2003). Severe acute
respiratory syndrome: Lessons from Singapore.
Emerging Infectious Diseases, 9, 1294-1298. Retrieved
January 1, 2004, from www.cdc.gov/ncidod/EID/
vol9no10/03-0388.htm.
Speck, R. S., & Wolochow, H. (1957). Studies on the
experimental epidemiology of respiratory infections,
VIII: Experimental pneumonic plague in Macacus
rhesus.Journal of Infectious Diseases, 100, 58-68.
Thomas, G. (1974). Air sampling of smallpox virus.
Journal of Hygiene, 73, 1-7.
Tuomi, T. (1985). Face seal leakage of half masks
and surgical masks. American Industrial Hygiene Asso-
ciation Journal, 46, 308-312.
Twu, S., Chen, T., Chen, C., Olsen, S. J., Lee, L.,
Fisk, T., et al. (2003). Control measures for severe
acute respiratory syndrome (SARS) in Taiwan. Emerg-
ing Infectious Diseases, 9, 718-720. Retrieved January
1, 2004, from www.cdc.gov/ncidod/EID/
vol9no6/03-0283.htm.
Wehrle, P. F., Posch, J., Richter, K. H., & Hender-
son, D. A. (1970). An airborne outbreak of smallpox
in a German hospital and its significance with re-
spect to other recent outbreaks in Europe. Bulletin of
the World Health Organization, 43, 669-679.
Wells, W. F. (1934). On air-borne infection. Study
II. Droplets and droplet nuclei. American Journal of
Hygiene, 20, 611-618.
Wells, W. F. (1955). Airborne contagion and air hy-
giene. Cambridge, MA: Harvard University Press.
... Certain pathogens may remain infective over longer distances [14]. However, defining the infective distance is difficult because it depends on particle size, the nature of the pathogen, and environmental factor [15]. Although data are not available to define specific infection risk from rosol transmission for most pathogens, some pathogens known to be transmitted over longer distances include coxiella burnetii (Q-fever) [15][16][17] and mycobacterium bovis (bovine tuberculosis-not present in Australia since 1997) [18]. ...
... However, defining the infective distance is difficult because it depends on particle size, the nature of the pathogen, and environmental factor [15]. Although data are not available to define specific infection risk from rosol transmission for most pathogens, some pathogens known to be transmitted over longer distances include coxiella burnetii (Q-fever) [15][16][17] and mycobacterium bovis (bovine tuberculosis-not present in Australia since 1997) [18]. Example of zoonotic disease transmitted through aerosol are Bordetella infection, Cryptococcosis, Hantavirus, Melioidosis, Nipah, plague, Psittacosis, Q-fever, streptococcosis, Tualremia etc. (www.cfsph.iastate.edu) ...
... Reverse Zoonoses: Infectious disease of people occasionally transferred to animals and then transferred back to people is termed as "reverse zoonoses" [15]. Examples are Tuberculosis [16], Mumps, Streptococcus pyogenes, infectious hepatitis, coryne bacterium diphtheria [17]. ...
... Moreover, the wet particles can dry very rapidly and transform to dry aerosol. For instance, the drying times for 100 µm and 50 µm droplets in air at 50% relative humidity are reported to be 1.3 and 0.3 s, respectively (Lenhart et al., 2004). On complete evaporation, the particles may be small enough to remain airborne in the indoor air flow. ...
... RH < 50%). We also note that our estimates on evaporation timescales are consistent with the values reported previously by others (Lenhart et al., 2004;Xie et al., 2007;Stadnytskyi et al., 2020). ...
Preprint
Full-text available
We provide research findings on the physics of aerosol dispersion relevant to the hypothesized aerosol transmission of SARS-CoV-2. We utilize physics-based modeling at different levels of complexity, and literature on coronaviruses, to investigate the possibility of airborne transmission. The previous literature, our 0D-3D simulations by various physics-based models, and theoretical calculations, indicate that the typical size range of speech and cough originated droplets (d < 20microns) allows lingering in the air for O(1h) so that they could be inhaled. Consistent with the previous literature, numerical evidence on the rapid drying process of even large droplets, up to sizes O(100microns), into droplet nuclei/aerosols is provided. Based on the literature and the public media sources, we provide evidence that the infected individuals could have been exposed to aerosols/droplet nuclei by inhaling them in significant numbers e.g. O(100). By 3D computational fluid dynamics (CFD) simulations, we give examples on the transport and dilution of aerosols (d<20microns) over distances O(10m) in generic environments. We study susceptible and infected individuals in generic public places by Monte-Carlo modeling. The model accounts for the locally varying aerosol concentration levels which the susceptible accumulate via inhalation. The introduced concept, 'exposure time' to virus containing aerosols is proposed to complement the traditional 'safety distance' thinking. We show that the exposure time to inhale O(100) aerosols could range from O(1s) to O(1min) or even to O(1h) depending on the situation. The Monte Carlo analysis provides clear quantitative insight to the exposure time in different public indoor environments.
... In this study, the experimental results were used as the basis for the selection of six aerosol size classes, 0.3, 0.5, 0.7, 0.9, 1.1, and 3 µm, and the number of exhaled aerosols was related to the size class. The moisture surrounding exhaled aerosol particles rapidly evaporates, drying the particles in less than a few seconds (Lenhart et al. 2004). Therefore, the particle sizes in this study were all postevaporation aerosol sizes, and aerosol particles in the evaporation process were not considered. ...
Article
Full-text available
Since December 2019, coronavirus disease (COVID-19) caused by severe acute respiratory syndrome coronavirus 2 (SARS-CoV-2) has become a great challenge to the world's public health system. Nosocomial infections have occurred frequently in medical institutions worldwide during this pandemic. Thus, there is an urgent need to construct an effective surveillance and early warning system for pathogen exposure and infection to prevent nosocomial infections in negative-pressure wards. In this study, visualization and construction of an infection risk assessment of SARS-CoV-2 through aerosol and surface transmission in a negative-pressure ward were performed to describe the distribution regularity and infection risk of SARS-CoV-2, the critical factors of infection, the air changes per hour (ACHs) and the viral variation that affect infection risk. The SARS-CoV-2 distribution data from this model were verified by field test data from the Wuhan Huoshenshan Hospital ICU ward. ACHs have a great impact on the infection risk from airborne exposure, while they have little effect on the infection risk from surface exposure. The variant strains demonstrated significantly increased viral loads and risks of infection. The level of protection for nurses and surgeons should be increased when treating patients infected with variant strains, and new disinfection methods, electrostatic adsorption and other air purification methods should be used in all human environments. The results of this study may provide a theoretical reference and technical support for reducing the occurrence of nosocomial infections.
... Quick evaporation makes the intermediate size droplets of RSSC to become airborne and stay floating in the air. For instance, the drying times for 50 and 100 μm droplets at 50% relative humidity are reported to be 0.3 and 1.3 s, respectively [13]. Even after complete evaporation, small airborne droplets can carry viruses as the usual size of viral pathogens is 25 nm to 5 μm and therefore a dried airborne may contain many of them. ...
Article
Full-text available
Airborne pathogen respiratory droplets are the primary route of COVID19 transmission, which are released from infected people. The strength and amplitude of a release mechanism strongly depend on the source mode, including respiration, speech, sneeze, and cough. This study aims to develop a simplified model for evaluation of spreading range (length) in sneeze and cough modes using the results of Eulerian-Lagrangian CFD model. The Eulerian computational framework is first validated with experimental data, and then a high-fidelity Lagrangian CFD model is employed to monitor various scale particles’ trajectory, evaporation, and lingering persistency. A series of Eulerian-Lagrangian CFD simulations is conducted to generate a database of bioaerosol release spectrum for the release modes in various thermal conditions of an enclosed space. Eventually, a correlation fitted over the data to offer a simplified airborne pathogen spread model. The simplified model can be applied as a source model for design and decision-making about ventilation systems, occupancy thresholds, and disease transmission risks in enclosed spaces.
... At the same time, the evaporation process changes the intermediate size droplets of RSSC to become airborne and stay floating in the air, which particularly highlights the role of ventilation and air humidity. For instance, the drying times for 50 μm and 100 μm droplets at a 50% relative humidity are reported to be 0.3 and 1.3s, respectively [36]. Even after a complete evaporation, small dried aerosol particles can potentially carry viruses as the usual size of viral pathogens is 25 nm to 5 μm [5]. ...
Article
COVID19 pathogens are primarily transmitted via airborne respiratory droplets expelled from infected bio-sources. However, there is a lack of simplified accurate source models that can represent the airborne release to be utilized in the safe-social distancing measures and ventilation design of buildings. Although computational fluid dynamics (CFD) can provide accurate models of airborne disease transmissions, they are computationally expensive. Thus, this study proposes an innovative framework that benefits from a series of relatively accurate CFD simulations to first generate a dataset of respiratory events and then develop a simplified source model. The dataset has been generated based on key clinical parameters (i.e., the velocity of droplet release) and environmental factors (i.e., room temperature and relative humidity) in the droplet release modes. An Eulerian CFD model is first validated against experimental data and is then interlinked with a Lagrangian CFD model to simulate trajectory and evaporation of numerous droplets in various sizes (0.1 μm–700 μm). A risk assessment model previously developed by the authors is then applied to the simulation cases to identify the horizontal and vertical spread lengths (risk cloud) of viruses in each case within an exposure time. Eventually, an artificial neural network-based model is fitted to the spread lengths to develop the simplified predictive source model. The results identify three main regimes of risk clouds, which can be fairly predicted by the ANN model.
... Quick evaporation makes the intermediate size droplets of RSSC to become airborne and stay floating in the air. For instance, the drying times for 50 and 100 μm droplets at 50% relative humidity are reported to be 0.3 and 1.3 s, respectively [13]. Even after complete evaporation, small airborne droplets can carry viruses as the usual size of viral pathogens is 25 nm to 5 μm and therefore a dried airborne may contain many of them. ...
Conference Paper
Full-text available
Airborne pathogen respiratory droplets are the primary route of COVID19 transmission, which are released from infected people. The strength and amplitude of a release mechanism strongly depend on the source mode, including respiration, speech, sneeze, and cough. This study aims to develop a simplified model for evaluation of spreading range (length) in sneeze and cough modes using the results of Eulerian-Lagrangian CFD model. The Eulerian computational framework is first validated with experimental data, and then a high-fidelity Lagrangian CFD model is employed to monitor various scale particles’ trajectory, evaporation, and lingering persistency. A series of Eulerian-Lagrangian CFD simulations is conducted to generate a database of bioaerosol release spectrum for the release modes in various thermal conditions of an enclosed space. Eventually, a correlation fitted over the data to offer a simplified airborne pathogen spread model. The simplified model can be applied as a source model for design and decision-making about ventilation systems, occupancy thresholds, and disease transmission risks in enclosed spaces.
... Для случая загрязнения воздуха биоаэрозолями ПДКрз (как правило) не установлены, замер загрязнённости воздуха может быть трудновыполним. Поэтому для выбора СИ-ЗОД предложили сопоставлять уровень риска и ожидаемые КЗ [7,8]. Для оценки риска используют сведения об интенсивности поступления загрязнений в воздух, кратности воздухообмена, свойствах микроорганизмов. ...
Article
Full-text available
Introduction. Healthcare practitioners are at increased risk of infection with infectious diseases, including the inhalation route. Healthcare practitioners use respirators of various designs providing different efficiency of protection. The purpose of the study was to improve efficiency of the respiratory protection of the healthcare practitioners in Russian Federation. There were analyzed available NIOSH publications, articles in journals Taylor & Francis, Oxford University Press, published materials of Federal Service for Supervision of Consumer Rights Protection and Human Welfare (Rospotrebnadzor), and western training manuals. Differences in the requirements of the legislation were identified that increase the risk of infection in healthcare practitioners. There are no methods for assessing the risk level, and there are no specific requirements for selecting the respirator’s type that corresponds to the risk level. The employer is not obliged to provide the fit test for all employees. The respirator must be used timely, so it should not negatively affect the worker. But the average carbon dioxide concentration can exceed the STEL by more than two times. The certification requirements for respirators do not correspond to the conditions of their use in the hospitals. Respirators were not certified as means of protection against bioaerosols. Conclusions. Identified shortcomings in the respiratory safety of health care workers show possible ways to improve their protection by harmonizing national legislation with the best of existing Western requirements.
Chapter
Respirators have been used for almost 2000 years, and the genesis of their technical development is actually the mid‐nineteenth century. The Bureau of Mines in 1919 initiated the first respirator certification program based in the United States and certified their first respirator based on laboratory testing. In 1995, NIOSH promulgated new certification regulations. This chapter notes that respiratory protective equipment (RPE) should be used only when all higher priority control steps are not technically or financially feasible. Thus, RPE continues to be an important component in many respiratory exposure control plans. This chapter also addresses the performance of RPE and its evaluation in the laboratory and the more recent reliance on testing in the workplace. A respirator program ensures that the RPE selected can provide adequate protection under the conditions of intended use by implementing a respiratory protection program.
Article
Full-text available
We provide research findings on the physics of aerosol and droplet dispersion relevant to the hypothesized aerosol transmission of SARS-CoV-2 during the current pandemic. We utilize physics-based modeling at different levels of complexity, along with previous literature on coronaviruses, to investigate the possibility of airborne transmission. The previous literature, our 0D-3D simulations by various physics-based models, and theoretical calculations, indicate that the typical size range of speech and cough originated droplets (d⩽20μm) allows lingering in the air for O(1h) so that they could be inhaled. Consistent with the previous literature, numerical evidence on the rapid drying process of even large droplets, up to sizes O(100μm), into droplet nuclei/aerosols is provided. Based on the literature and the public media sources, we provide evidence that the individuals, who have been tested positive on COVID-19, could have been exposed to aerosols/droplet nuclei by inhaling them in significant numbers e.g. O(100). By 3D scale-resolving computational fluid dynamics (CFD) simulations, we give various examples on the transport and dilution of aerosols (d⩽20μm) over distances O(10m) in generic environments. We study susceptible and infected individuals in generic public places by Monte-Carlo modelling. The developed model takes into account the locally varying aerosol concentration levels which the susceptible accumulate via inhalation. The introduced concept, ’exposure time’ to virus containing aerosols is proposed to complement the traditional ’safety distance’ thinking. We show that the exposure time to inhale O(100) aerosols could range from O(1s) to O(1min) or even to O(1h) depending on the situation. The Monte-Carlo simulations, along with the theory, provide clear quantitative insight to the exposure time in different public indoor environments.
Book
Full-text available
The purpose of this guidebook is to provide detailed information for field investigations to identify the cause of death of livestock when attacks by carnivores are suspected. It will assist damage inspectors, agricultural advisers, and others in determining the species of wildlife that cause damage. Additionally, this guide will help users recognize wildlife signs at damage sites, and for collecting evidence for further analysis. It will also help users to protect themselves against zoonoses, which might infect people when being in contact with animal carcasses.
Article
Full-text available
Biological weapons are not new. Biological agents have been used as instruments of warfare and terror for thousands of years to produce fear and harm in humans, animals, and plants. Because they are invisible, silent, odorless, and tasteless, biological agents may be used as an ultimate weapon-easy to disperse and inexpensive to produce. Individuals in a laboratory or research environment can be protected against potentially hazardous biological agents by using engineering controls, good laboratory and microbiological techniques, personal protective equipment, decontamination procedures, and common sense. In the field or during a response to an incident, only personal protective measures, equipment, and decontamination procedures may be available. In either scenario, an immediate evaluation of the situation is foremost, applying risk management procedures to control the risks affecting health, safety, and the environment. The microbiologist and biological safety professional can provide a practical assessment of the biological weapons incident to responsible officials in order to help address microbiological and safety issues, minimize fear and concerns of those responding to the incident, and help manage individuals potentially exposed to a threat agent.
Article
The study of aerosols in indoor air and the assessment of human exposure to aerosols are relatively recent activities. The terms indoor air and exposure assessment refer primarily to nonindustrial settings, such as homes, offices, and public-access buildings (e.g., museums, airport terminals, retail stores). Although many occupational settings are 'indoors', the aerosol concentrations and constituents, airflow regimes, and turbulence levels pose related, but different, aerosol measurement constraints. Until recently, it was commonly believed that the quality of indoor air was superior to that of the outdoor (ambient) air nearby. Several factors have influenced the apparent deterioration of indoor air quality: life-styles have changed; building construction techniques have changed; and people have become more concerned about environmental tobacco smoke (ETS).
Article
Objective: To evaluate the distribution of Bordetella pertussis and respiratory syncytial virus (RSV) in the hospital setting. Design: Air samples were collected using filters in the hospital rooms of 12 children with pertussis and 27 children with RSV infection. Material eluted from these filters was subjected to RSV- and B pertussis-specific polymerase chain reaction (PCR) amplification. Setting: Patients were hospitalized in private rooms in one of two referral centers, a university teaching hospital and a university-affiliated private children's hospital. Patients: 12 children (16 days-3 years of age) with documented pertussis infection and 27 patients (10 days-7 years of age) with documented RSV infection. Results: B pertussis DNA was detected in 7 (58%) of 12 rooms housing pertussis patients and in 16 (25%) of 63 total samples. B pertussis DNA was detected as far as 4 m away from the patient's bedside. The detection of B pertussis DNA in air samples did not change over the short duration of hospitalization. RSV RNA was detected in 17 (63%) of 27 rooms housing RSV-infected patients and in 32 (22%) of 143 total samples. RSV RNA was detected at distances as far as 7 m from the patient's bedside and for up to 7 days of hospitalization. Conclusions: Using PCR-based detection methods, B pertussis DNA and RSV RNA both can be detected in air samples from the hospital rooms of infected patients. Both can be detected at large distances from a patient's bedside in a minority of cases. These detection methods are suitable for further studies of control measures used to contain nosocomial infections caused by both B pertussis and RSV.