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OCR for page 239
Biological Disposition
of Airborne Particles:
Basic Principles en cl
Application to Vehicular
~ · -
~mlsslons
RICHARD B. SCHLESINGER
New York University Medical Center
Structure of the Respiratory Tract / 240
Upper Respiratory Tract / 240 Tracheobronchial
Tree / 241 Pulmonary Region / 244 Research
Recommendations / 246
Ventilation / 246
Ventilatory Parameters / 246 Comparative Aspects of
Ventilation / 248 Airflow Patterns / 248 Research
Recommendations / 249
Deposition of Inhaled Particles in the Respiratory Tract / 250
Deposition Mechanisms and Controlling Factors / 250 Measurement
of Deposition / 253 Factors Modifying Deposition / 258
Localized Patterns of Deposition / 259 Mathematical
Modeling / 260 Research Recommendations / 262
Retention of Deposited Particles / 263
Clearance Mechanisms: Basic Structure and Function / 263 Clearance
Kinetics / 266 Factors Modifying Clearance / 272 Research
Recommendations / 273
Disposition of Vehicular Particulate Emissions / 275
Diesel Exhaust Particles / 275 Metals / 276
Sulfates / 280 Research Recommendations / 281
Summary 1 283
Summary of Research Recommendations: Discussion / 284
Summary of Research Recommendations: Priorities / 285
Air Pollution, the Automobile, and Public Health. @) 1988 by the Health Effects
Institute. National Academy Press, Washington, D.C.
239
OCR for page 240
240
Biological Disposition of Airborne Particles
The primary route of exposure to motor
vehicle emissions is inhalation. The respi-
ratory tract has a large internal surface area
that is directly and continually exposed to
10,000 to 20,000 liters of ambient air in-
haled daily, making it a potential target site
for exhaust products. In addition, because
the barrier between inhaled air and the
pulmonary bloodstream is very thin, the
respiratory tract is also an efficient portal of
entry into the general circulation.
A large fraction of emissions is either
directly released in particulate form or be-
comes adsorbed onto the surface of other
ambient particles. The disposition of in-
haled particles, and any adsorbed constitu-
ents, determines the dose delivered to tar-
get tissues. However, their ultimate fate and
any potential hazard depend upon various
interacting parameters: the physicochemical
characteristics of the particles, the amount
that actually deposits in the respiratory tract,
and the rates and routes by which deposited
material is cleared from the respiratory tract
or translocated to other organs.
Particles derived from motor vehicles do
not have unique properties that influence
their deposition or clearance. Thus, their dis-
position can be assessed in general terms.
This chapter is a review of the biological dis-
position of inhaled particulate matter in
terms of the factors that influence and control
its deposition, clearance, translocation, and
ultimate retention. The fate of specific non-
organic particles found in automobile ex-
haust will be assessed as examples of the dis-
position of toxicologically relevant material.
Some of the information presented is
based on studies with humans, but much is
derived from experiments with laboratory
animals. Since human experimentation is
precluded in many instances and often
yields only limited data, surrogate animal
models are needed. However, extrapola-
tion from animal studies requires informa-
tion on similarities and differences between
species that may influence the disposition of
inhaled materials. Thus, an attempt has
been made to interrelate and integrate hu-
man data with that obtained with experi-
mental animals and, in some cases, even
. . .
Wlt 1 in vitro systems.
The chapter is divided into five major
sections. The first describes the anatomy of
. . .
t :le respiratory tract, since airway structure
is a major determinant of particle disposi-
tion. The second section discusses the as-
pects of ventilation important in exposure
assessment, including scaling for different
· ~1 . ~ - ~ . - ~ ·1 ~
species.
l he third section describes the
physical mechanisms by which inhaled par-
tlcles deposit in the respiratory tract, their
controlling influences and modifying fac-
tors. It critically reviews the available data
for total and regional deposition in humans
and experimental animals and provides a
comparative analysis of interspecies depo-
sition patterns. The fourth section discusses
the structure, physiology, kinetics, and
modifiers of the mechanisms by which
deposited particles are cleared from, or
translocated and retained within, the respi-
ratory tract. The fifth section discusses the
fate of specific nonorganic particles of rel-
evance to automobile exhaust toxicology,
that is, diesel particles, metals, and sulfates.
In all five sections, knowledge gaps are
highlighted and recommendations for re-
search to fill these gaps are presented.
Structure of the
Respiratory Tract
The respiratory tract is divided into two
. . . .
sections accorc lug to tunctlon: one IS con-
cerned with transporting air from the ex-
ternal environment to the sites of gas
exchange and consists of the upper respira-
tory tract and the tracheobronchial tree; the
other, the pulmonary region, is involved in
gas exchange.
Upper Respiratory Tract
This region originates at the nostrils and
mouth and extends through the larynx; a
diagram of the human upper respiratory
tract is shown in figure 1. Air entering the
nostrils passes first through the vestibule,
the narrowest cross-section in the entire
nasal region, before entering the main nasal
passages. These consist of two airways
separated almost symmetrically by the na-
sal septum. They are convoluted (due to
OCR for page 241
Richard B. Schlesinger
Vestibule
.....
t\ \\ \ ~ \_Trachea
Figure 1. Diagram of the human upper respiratory
tract.
the folds of the nasal turbinates), down-
ward-curving shelf-like structures, result-
ing in a large surface area and a relatively
narrow distance between opposing airway
walls. Here, exchange of heat and moisture
modify the temperature and humidity of
the inhaled air. The nasopharynx begins at
the posterior end of the turbinates, where
the septum ends and the nasal passage
narrows and turns downward. Although
the basic structure of the nasal airways is
similar in humans and most other mam-
mals, there are considerable interspecies
differences in the relative position, shape,
and size of individual components, as
shown in figure 2. For example, the naso-
pharynx in the rat encompasses a greater
percentage of the total length of the nasal
passages than in the human, whereas that
in rabbits and dogs is intermediate between
rats and humans.
The oral passages begin at the mouth and
are characterized by much greater inter-
and intraindividual variation in shape and
cross-section than the nasal passages. At the
posterior of the mouth, inhaled air enters
the oropharynx. The oro- and nasopharynx
join to form the hypopharynx, an airway
that extends to the entrance of the larynx.
The latter extends to the trachea and has a
variable cross-section depending upon the
rate of airflow through it.
241
r _Hypopharynx Figure 2. Silicone rubber replica casts of the naso
) pharyngeal region of different species: (A) human; (B)
_~:arunx rabbit; (C) rat; (D) guinea pig; (E) hamster; (F) ba
boon; scale in cm. (Adapted with permission from Patra
1986, and from Hemisphere Publishing Corporation.)
Tracheabronchial Tree
The tracheobronchial tree consists of air-
ways from the trachea through the terminal
bronchioles. The trachea divides into two
main bronchi which then enter the lungs at
the hilar region. These main bronchi fur-
ther subdivide into smaller airways. Sup-
port for the trachea and bronchi are derived
from cartilagenous rings or plates. As the
bronchial tree proceeds distally, the carti-
lage eventually disappears, and these air-
ways the bronchioles are supported by
smooth muscle. In humans, the transition
from bronchi to bronchioles occurs in air-
ways of~1-mm diameter.
Simplistically, the tracheobronchial tree
can be considered to be a system of tubes
connected at specific division points. In
most cases, division is by dichotomy,
whereby a single branch (the parent) gives
.% j ,,,
A B
BEAN\ ;7
Ok
(,/
Figure 3. Schematic diagram of tracheobronchial
tree branching patterns: (A) human lung; (B) mono-
podial system common in experimental animals.
OCR for page 242
242
Biological Disposition of Airborne Particles
rise to two branches (the daughters). To
describe this structure, the position of an
individual airway is usually assigned a code
number. There are two basic coding sys-
tems: the numbering of divisions up from
distal end branches or, alternatively, down
from the trachea. For example, in the of-
ten-used Weibel ordering system (Weibel
1963), each branching division is known as
a generation; the trachea is generation 0,
and each distal division increases by one
number.
In a dichotomous branching system, the
pattern can vary in terms of the degree of
symmetry (figure 3~. If both daughters
have the same diameter and length, and
branch from the parent at the same angle,
the mode of division is known as regular or
symmetrical. If the two daughters differ
from each other in one or more dimen-
sions, the mode of branching is termed
irregular or asymmetrical, the extreme case
of which is monopody. In a monopodial
branching system, the larger-diameter
daughter (major daughter) may not be eas-
ily distinguishable from the parent since the
change in diameter and direction from the
parent may be negligible.
A major difference in respiratory tract
anatomy between humans and most other
mammals commonly used in inhalation
studies is in the pattern of bronchial airway
branching. Figure 4 shows casts of the
upper bronchial tree in humans and in a
number of other species, and figure 5 pre-
sents a quantitative analysis that allows
characterization of branching patterns. In a
regular dichotomous branching system, the
ratio of daughter diameters is 1, whereas in
a perfect monopodial branching system,
the ratio of major daughter diameter to
Figure 4. Silicone rubber replica casts of the tra-
cheobronchial tree of different species. (A) human; (B)
baboon; (C) dog; (D) rhesus monkey; (E) rabbit; (F)
guinea pig; (G) rat; (H) hamster; (I) mouse. Both
photos are reproduced here at the same scale, given in
inches at the bottom. (Adapted with permission from
Patra 1986, and from Hemisphere Publishing Corpo-
ration. )
parent diameter is 1. The human bronchial
tree, at least for the first six generations,
exhibits the most symmetrical branching of
all of the species shown, whereas the dog's
bronchial tree is almost ideally monopodal.
The other species exhibit various degrees of
irregularity. Recent qualitative observa-
tions on the tracheobronchial trees of two
nonhuman primates-the rhesus monkey
and the baboon suggest a branching pat-
tern that is more irregular than that of
humans, but not to the extent of the exper-
imental animal species shown in figure 5
(Patra 1986~. But although there may be
striking interspecies differences in the upper
bronchial tree, the branching patterns in
most mammals tend to approach more
regular symmetry in distal conducting air-
ways.
An important difference between regu
OCR for page 243
Richard B. Schlesinger
A ~ Major/minor
· Major/parent
· Minor/parent
c', 3.0
o
Go 2.c
LU
LU
~ 1.0
-
c`' 3.0
o
~ 2.0
I; 1.0
6
n
90:
u,
at, 60
Al
~ 30
an
At:
90
Hamster
B · Major
~ Minor
Human
Hamster
~ 60 _ /
L9U ~
, 30 ~ l:
0
1 2 3 4 5 6
Herman
AIRWAY GENERATION
Human
_:
Rabbit
Dog
Rat
l l l l l l
1 2 3 4 5 6
Dog
- iV:
I'
Rat
1~ ~
1 2 3 4 5 6 1 2 3 4 5 6
AIRWAY GENERATION
Figure 5. Morphometric relationships for the bronchial trees of different species.
Each panel is derived from measurements of a single silicone rubber cast. (A) Ratios
of airway diameters as a function of branching generation; (B) ratios of branching
angles as a function of generation. (Adapted with permission from Schlesinger and
McFadden 1981 .)
lar and irregular dichotomous branching
modes concerns the number of airways
between the trachea and the terminal bron-
chioles. In a regular dichotomous branch-
ing system, the number of divisions and,
243
therefore, the path length, between the
trachea and the most distal conducting air-
ways is the same along any pathway. In
addition, all airways at any branch level
have exactly the same dimensions. In an
OCR for page 244
244
Biological Disposition of Airborne Particles
Table 1. Airway Path Lengths
Number of Airway Divisions (Generations)a
Mean Range of Means
Species (for entire lung) (for individual lobes) Reference
Human 17 Weibel (1963)
Human 15 1017 Schum et al. (1976)
Rat 15 11-19 Raabe et al. (1977)
Hamster 14 10-18 Raabe et al. (1977)
Dog (beagle) 18 15-21 Schum et al. (1976)
a From trachea through terminal bronchioles.
SOURCE: Adapted with permission from Schlesinger and McFadden 1981.
irregular dichotomous system, the number
of branch divisions from the trachea to each
distal bronchiole is not the same along
every pathway, and not all airways at a
given branch level have the same dimen-
sions. Table 1 presents the average number
of branching generations from the trachea
through the terminal bronchioles for vari-
ous species. Humans have the narrowest
range of branching generations, a reflection
of the greater symmetry of their lungs.
Because of the complexity of airway
branching structure, the geometry of the
tracheobronchial tree has been represented
by models; these are idealizations derived
from experimental data, usually from mea-
surements performed on castings prepared
from actual lungs. One of the most widely
used human structural models is the sym-
metrically dichotomous Weibel Model A
(Weibel 1963~. This is a 23-generation sys-
tem, with generations (}16 representing
conducting airways. Although the assump-
tion of regular dichotomy simplifies the
treatment of morphometric data, the actual
bronchial tree is asymmetrical, and a num-
ber of models of human airways that ac-
count for asymmetry have been described
(Horsfield and Cumming 1968; Olson et al.
1970; Horsfield et al. 1971; Parker et al.
1971~. In addition, Phalen and coworkers
(1978) and Yeh and Schum (1980) devel-
oped structural models of the human lung
which consist of"typical pathways," based
on mean dimensions, for each lobe within
the lung. Although the models were devel-
oped with symmetrical branching within
each lobe, they do account for the asym-
metry, and resultant variable path length,
between different lobes. Most of the tra
cheobronchial models have been based
upon measurements made in only one
lung. The very limited data base suggests
that there is significant variability in airway
dimensions between individuals (Nikiforov
and Schlesinger 1985), but the only model
that accounts for this is a statistical descrip-
tion of the tracheobronchial tree based upon
the Weibel geometry (Soon" et al. 1979~.
Structural models of the bronchial tree
have also been developed for experimental
animals. These include symmetrical dichot-
omous models for the rabbit (Kliment
1974), the rat (Kliment 1973), and the
guinea pig (Kliment et al. 1972) and typical
pathway models for the dog, the rat, and
the hamster (Yeh 1980~.
Pulmonary Region
The pulmonary region extends from the
respiratory bronchioles through the alveoli
and contains airways involved in gas ex-
change between the air and blood (figure
6a). In the human lung, the final generation
of airways that merely conduct air the
terminal bronchioles branch into several
generations of respiratory bronchioles,
which are characterized by the presence of
alveoli. The degree of alveolarization in-
creases toward the lung periphery; when
the airway becomes totally alveolarized, it
is termed an alveolar duct. This may
branch into other ducts, or into blind-
ended alveolar sacs. The adult human lung
contains ~ 375 million alveoli, the number
varying with body size, and the average
alveolar diameter is 25(}300 ,um. This re-
sults in a total alveolar surface area on the
order of 150-180 m2 (Weibel 1980~.
OCR for page 245
Richard B. Schlesinger
A
\' ''''":
245
B
~Type I alveolar cell -~~
Surface-active layer
(surfactant) (~7
\~1
Terminal bronchioles
Respiratory bronchioles
Alveoli
Alveolus pair space) <~: ~
Type It alveolal$y :(
~ Intern 4~\
Figure 6. (A) Diagram of the human airways in the pulmonary region; (B) diagram of the cellular makeup and
surrounding structures of the alveolus.
There are large interspecies differences in
the gross structure of the pulmonary region
(Gehr et al. 1981; Tyler 1983~. The number
of branching generations of respiratory
bronchioles and alveolar ducts varies, and
some species appear to have no respiratory
bronchioles. The degree of alveolarization
of the respiratory bronchioles also differs,
as does alveolar size and total alveolar sur-
face area, the latter increasing in direct
proportion to body mass.
The alveolar surface is lined with a con-
tinuous layer of two distinct cell types
(figure 6b). About 9~95 percent is covered
by type I cells, which are characterized by a
central nucleus surrounded by cytoplasm
stretching out in thin winglike processes to
form part of the alveolar wall. The remain-
ing surface is covered by cuboidal-shaped
type II cells, which are actually more numer-
ous than the type I cells. The relative num-
bers of these cell types, as well as the percent-
age of the alveolar surface covered by each,
are similar in humans and most other mam-
mals (Crapo et al. 1983; Gehr 1984~.
The alveoli are supported by a frame-
work of connective tissue termed the inter-
stitium. Capillary endothelial cells are
joined through the interstitium to alveolar
epithelial cells, to form the "alveolo-cap-
illary membrane." This membrane is about
2 ,um thick in humans, but appears to be
thinner in most experimental animals
(Meessen 1960; Crapo et al. 1983; Gehr
1984~. The interstitium and associated
structures form the part of the lung known
as the parenchyma. This region also in-
cludes the pulmonary lymphatic vessels.
The lungs contain two lymphatic net-
works. One set (superficial or pleural net-
work) is located within the connective tis-
sue layer of the visceral pleura, whereas the
other (deep or peribronchovascular net-
work) consists of interconnecting vessels
within the connective tissue surrounding
both the airways (to the level of the respi-
ratory bronchioles) and the pulmonary vas-
cular system. A plexus of vessels connects
the two sets. In both systems, the network
begins as blind-ended capillaries and fluid
flows toward the hilar region of the lung.
Many larger lymphatic vessels are inter-
spersed with nodes (encapsulated aggre-
gates of lymphoid tissue); the most prom-
inent of these are located along the trachea
and main bronchi, and at branching sites
between these airways. More diffuse lym-
phoid aggregates occur near the branching
regions of smaller bronchi and bronchioles.
Eventually, the entire pulmonary lym
OCR for page 246
246
Biological Disposition of Airborne Particles
phatic system drains into the general ve
. .
nous c~rcu anon.
Research Recommendations
Quantitative anatomy or morphome-
try of the respiratory tract is essential for
understanding the dosimetry of inhaled
particles. The structure of the various com-
ponents of the respiratory tract influences
the airflow and, thus, the resultant pattern
of particle deposition and the distribution
of sites of potential damage. Morphometry
must be assessed in humans as well as
experimental animals, the latter so as to
assist in the extrapolation of toxicologic
data to humans. Data are available for
normal adult humans and some other spe
. . . .
cles, rut cntlca gaps remain.
· Recommendation 1. Variability in
morphometry of the tracheobronchial and
pulmonary regions in normal humans as
well as experimental animals (including dif-
ferent strains) should be studied. Better
statistical descriptions of interindividual
variation at all levels of the respiratory tract
are needed to validate conclusions drawn
from current theoretical or empirical dep-
osition models, which are generally based
upon a single morphometric model.
· Recommendation 2. Lung morphom-
etry should be assessed in potentially "sus-
ceptible" subsegments of the human pop-
ulation: children, the elderly, and people
with respiratory disease. Although data are
becoming available on the morphometry
of children's lungs at different ages, these
are not yet sufficient to develop a compre-
hensive morphometric model describing
growth of the tracheobronchial tree. No
information exists at all for assessment of
morphometric changes due to aging or
disease.
Recommendation 3. Comparative
morphometry of human and animal upper
respiratory tracts should be assessed. Be-
cause of large interspecies differences in the
nasopharyngeal region, more quantitative
information is needed to allow better com-
parison with that in humans. For example,
rodents have essentially a straight pathway
from the nostrils to the trachea, a situation
radically different from that in humaps and
nonhuman primates. In humans, more de-
tailed information on dimensions of the
oral passages under different ventilatory
conditions is also needed to assess particle
removal by the upper respiratory tract.
~ Recommendation 4. Comparative
structure and physiology of human and
animal pulmonary lymphatic systems
should be studied. This knowledge is
needed for better comparisons of particle
clearance by this route in humans and ex-
perimental animals.
Ventilation
Ventilatory Parameters
Ventilation is the movement of air in and
out of the respiratory tract and is a factor in
determining the amount of an exposure
atmosphere that is actually inhaled. Venti-
latory parameters also affect the deposition
of particles once inhaled.
The amount of air inspired (or expired)
during a normal breath is the tidal volume
~ VT); it averages 450-600 ml in resting
healthy males and slightly less for females.
The fraction of the VT that does not reach
the alveolated airways about 150-200
ml in resting males and 120-160 ml in
females is termed the anatomic dead
space volume ( VDanac)
Not all of the inspired air reaching the
pulmonary region is equally effective in
oxygenating the blood, since air may enter
alveoli that are ventilated but poorly per-
fused. The portion of VT that does not
equilibrate with gas pressure in the pulmo-
nary capillary blood is the alveolar dead
space volume (ED, ). The total volume of
inhaled air that does not participate in gas
exchange, VDanac + VDa,v, is termed the total
or ph,vs~olog~cal dead space ~ ED ~
During expiration, air within the tra-
cheobronchial tree largely from the pre-
vious inspiration is expelled along with
some alveolar air which is a mixture from a
number of inspirations. Particles inhaled
OCR for page 247
Richard B. Schlesinger
247
into the pulmonary region can therefore be
exhaled over a number of breaths. Thus,
the time available to deposit inhaled parti-
cles in the conducting airways is fairly short
(a few seconds), whereas the residence time
in pulmonary air may be longer (about a
minute).
Total ventilation ~ VE), or minute volume
(MV), is defined as the volume of air
expired each minute and is equal to VT
times the breathing frequency by. The av-
erage f during normal quiet breathing in
adults is 11-17 breaths/min, and the rest-
~ng VE averages ~10 liters/mint The VE
consists of anatomic dead space ventilation
(VD~nat) and total alveolar ventilation (VA),
the latter being the amount of air entering
the pulmonary region each minute. The
effective portion of VA that participates in
gas exchange is equal tOf(VT- VDIO').
Ventilation is affected by numerous ex-
ogenous factors such as altitude, ambient
temperature, and smoking, as well as
endogenous factors such as body size. Two
of the major modifiers in any particular
individual are physical activity and age.
Physical Activity. Healthy humans at
rest normally breath through the nose, but
when respiratory demand increases above a
certain level there is a shift to oronasal
(combined nose and mouth) breathing.
Maximum inspiratory nasal airflow occurs
at a VE of 30 40 liters/min (Swift and
Proctor 1977; Niinimaa et al. 1980), at
which point ~40 60 percent of total air-
flow occurs through the nose. As respi-
ratory demand increases further, the pro-
portion of air entering the mouth increases,
but even at high demand the oral path-
way accounts for no more than 60 per-
cent of the inhaled air (Swift and Proctor
1987~.
With mounting respiratory demand, VT
and f increase, and the maximum volume
of air that can be inhaled per minute, or
the maximum voluntary ventilation, may
rise to more than 10 times the resting
ventilatory level. As breathing frequency
increases, expiratory time diminishes, but
inspiratory time remains relatively con-
stant. Furthermore, respiratory pauses, the
gaps between expiration and inspiration
which can occupy 25 percent of the breath-
ing cycle in resting individuals, become
shorter with increasing level of activity.
Growth and Aging. The volume of air in
the lungs and the ventilatory capacity de-
pend on body and lung size and, thus,
increase with growth from childhood. In
addition, the contribution of VT and f to
total ventilation also changes; VT increases
while f decreases until maturity is reached
(Mauderly 1979~.
Ventilatory function reaches a peak be-
tween the ages of 20 and 35 and then begins
to decline. Although various models have
been proposed to describe these changes,
they differ in their assumptions about the
rate of functional decline (Buist 1982~. Fur-
thermore, most of the reported data for
age-related changes in lung function are
derived from cross-sectional population
studies and may not reflect the true aging
process, especially since these studies may
be measuring the heartiest survivors. The
best way to avoid possible bias is to exam-
ine true aging patterns in longitudinal stud-
ies in which the same people are tested over
a number of years. Such analyses are scarce,
and those that do exist have measured only
a few parameters (Fowler 1985~.
Changes in lung function with aging are
the result of deterioration of the lung tissue
itself, a decrease in the strength of the
respiratory muscles, and an increase in the
stiffness of the thoracic cage. The time
course varies from individual to individual
and may be aggravated by chronic pollut-
ant exposure. Some ventilatory indices are
affected by age, whereas others are not.
Figure 7 shows a diagram of the various
divisions into which the volume of air in
the lungs may be separated. With age,
functional residual capacity (FRC) and re-
sidual volume (RV) increase, whereas vital
capacity (VC), inspiratory capacity (IC),
and expiratory reserve volume (ERV) de-
crease. Anatomic dead space ~ VD ~ in-
creases w~th age because of a decrease ~n
lung elasticity and a resultant increase in
lung volume at the same pressure differen-
tials.
Aging is associated with regional in-
equalities in the distribution of ventilation
OCR for page 248
248
Biological Disposition of Airborne Particles
~I
AN I
Figure 7. Diagram of subdivisions of lung volumes
as measured with a spirometer. A typical spirometer
tracing is shown on the right. TLC = total lung
capacity, VC = vital capacity, RV = residual volume,
FRC = functional residual capacity, IRV = inspira-
tory reserve volume, ERV = expiratory reserve vol-
ume, VT = tidal volume, and IC = inspiratory
capacity.
and a decrease in the uniformity of perfu-
sion (Holland et al. 1968~. Nonuniform
mixing of inspired air may result when
sections of the lungs communicate poorly
with others and, because of this, some alve-
olar regions may not be continuously venti-
lated during normal tidal breathing. Non-
uniform perfusion results in an increase
in VD} which, together with the increase
In VD, results In an ag~ng-related rise
in VD . Although this does not affect rest-
ing levels of BE, which show no major
change with aging, the ability of the lungs
to respond to increased activity is altered,
and maximum voluntary ventilation de-
clines by about 30 percent between ages 30
and 70.
Comparative Aspects of Ventilation
Since much of the toxicologic work with
inhaled particles involves experimental an-
imals, it is essential that their respiratory
mechanics be quantitated. Various animal
data exist (see, for example, Guyton 1947;
Spell 1969), but the methods used to obtain
them were not standardized, so there is
much variability, even for similarly sized
animals of the same species. "Repre-
sentative" ventilatory values for a particu-
lar species are therefore difficult to snecifv.
so generalized values based on scaling pro
cedures are used. Scaling is based on the
principle that respiratory mechanical prop-
erties may be related to body size or mass in
some consistent fashion, even though there
may be interspecies differences in the mech-
anisms that determine these properties.
This allows quantitative comparisons of
function between animals of different sizes,
within or between species. Scaling makes
use of dimensional or dimensionless pa-
rameters that either remain constant with
body size or can be related to body size by
some proportionality factor (Leith 1983~.
For example, VE is proportional to body
mass (M) raised to the 3/4 power, whereas
lung volumes, such as VT, tend to vary
with M to the first power. Similarly,
breathing frequency is proportional to
M-~/4, whereas the ratio of VD to VT is
Independent of body size.
Stahl (1967), after an extensive literature
search, developed predictive equations re-
lating respiratory variables in mammals to
body weight. These equations can be used
to scale values between animals of different
species as well as between individuals of
different body weights within one species,
as long as the animals are in comparable
physiological states. Scaling is not a precise
technique, however, and is only as good as
the values upon which the exponents and
proportionality factors are based. For ex-
ample, many of these values have been
obtained in anesthetized animals, in which
actual lung volumes and ventilation may be
less than normal (Sweeney et al. 1983~.
Airflow Patterns
Patterns of airflow in the conducting air-
ways are a major determinant of particle
deposition sites. Basic principles of airflow
are presented by Ultman (this volume).
Aspects of airflow critical to particle depo-
sition are addressed below.
Within straight tubes, two main types of
flow may occur: laminar and turbulent. In
laminar flow, gas molecules move in par-
allel as a smooth stream, with the highest
velocity occurring at the center of this
stream. The flow can be imagined as con-
centric layers of air sliding or telescoping
lengthwise along each other, with no trans
OCR for page 249
Richard B. Schlesinger
249
verse mixing between layers. In turbulent
flow, gas molecules are in an agitated state,
and there is erratic mixing of concentric
layers. Random secondary flows (eddies)
are superimposed on the average longitudi-
nal motion of flow velocity. Flow that is
partially laminar and partially turbulent is
termed transitional.
The type of flow that occurs depends
upon the strength of the inertial forces in
the moving air in relation to the frictional
and viscous forces acting on it. For exam-
ple, turbulence occurs when the former
exceed the latter. Airflow may thus be
described in terms of the ratio of inertial
forces to viscous and frictional forces,
which is expressed as the dimensionless
Reynolds number (Re). The Reynolds
number depends on the geometry of the
conduit through which the air passes and
the velocity of airflow, and flow character-
istics change as Re passes certain critical
values. Thus, for steady flow in a straight,
smooth-walled, circular tube, flow will be
laminar when Re is less than 2100, transi-
tional when Re is between 2100 and 4000,
and fully turbulent when it exceeds 4000
(Hinds 1982~.
Within the respiratory tract, bends, bi-
furcations, constrictions, surface roughness
and convolutions, and other features of
airway shape that add inertial forces may
lead to turbulent flow at a velocity lower
than that at which turbulence would be
initiated in a smooth, straight, obstacle-free
tube having the same cross-section. Thus,
flow instability and turbulence may occur
in the upper respiratory tract and upper
tracheobronchial tree at Reynolds numbers
well below 2100 (West and Hugh-Jones
1959; Dekker 1961; Sekihara et al. 1968;
Olson et al. 1973; Swift and Proctor 1977~.
Turbulence is also produced by the contin-
uous acceleration and deceleration of air
during the breathing cycle (Lakin and Fox
1974~. But although turbulent flow gener-
ated in the upper airways upon inspiration
may be propagated into a few generations
of downstream bronchi, air velocity de-
creases with depth into the lung, and in the
smaller conducting airways, flow is always
laminar.
Because of structural differences between
the tracheobronchial trees of humans and
most other mammals, one would expect
differences in resultant flow patterns. For
example, the trachea of most mammals is
much longer relative to its diameter than is
the human trachea. Thus, any turbulence
introduced by flow through the larynx is
much less likely to persist into the down-
stream bronchi of nonhuman mammals.
Unfortunately, there are few data on air-
flow patterns in the airways of most com-
monly used experimental animals (see, for
example, Snyder and Jaeger 1983~.
Research Recommendations
Ventilatory patterns and airflow dynamics
are critical determinants of dose to the
respiratory tract from inhaled particles.
The following important gaps In our
knowledge of ventilation in humans and in
experimental animals should be filled.
~ Recommendation 5. Patterns and dis-
tribution of airflow in the tracheobronchial
tree of healthy adult experimental animals
and humans should be determined. This
information is important for the develop-
ment of deposition models and for the
extrapolation of results of toxicologic stud-
ies to humans.
Recommendation 6. Effects of aging
on ventilation in humans and experimental
animals should be determined by use of
longitudinal studies of humans and experi-
mental animals involving numerous venti-
latory parameters. In animals, a cross-cor-
relation of age equivalencies between
species should be performed, so that pa-
rameters of toxicologic studies may be bet-
ter related to lung function in humans.
Recommendation 7. Ventilatory me-
chanics and airflow in children should be
analyzed. Although data are available for
some stages of growth, there is a gap
between birth and ~9 years of age.
~ Recommendation 8. Flow patterns in
the upper respiratory tracts of experimental
animals and humans should be studied.
Most experimental animals are obligate na
OCR for page 288
288
ics of bronchial clearance in humans and donkeys,
In: Inhaled Particles III (W. H. Walton, ed.), vol. 1,
pp. 165-180, Unwin Bros., Surrey, England.
Albert, R. E., Lippmann, M., Peterson, H. T., Jr.,
Sanborn, K., and Bohning, D. E. 1973. Bronchial
deposition and clearance of aerosols, Arch. Intern.
Med. 131:115-127.
Altshuler, B., Yarmus, L., Palmes, E. D., and Nel-
son, N. 1957. Aerosol deposition in the human
respiratory tract, Arch. Ind. Health 15:293-303.
Altshuler, B., Palmes, E. D., and Nelson, N. 1966.
Regional aerosol deposition in the human respira-
tory tract, In: Inhaled Particles and Vapours II (C. N.
Davies, ed.), pp. 323-335, Pergamon Press, Ox-
ford, England.
Aranyi, C., Andres, S., Ehrlich, R., Fenters, J. D.,
Gardner, D. E., and Waters, M. D. 1977. Cytotox-
icity to alveolar macrophages of metal oxides ad-
sorbed on fly ash, In: Pulmonary Macrophage and
Epithelial Cells (C. L. Sanders, R. P. Schneider,
G. E. Dagle, and H. A. Ragan, eds. ), CONF-
760927, pp. 5~65, National Technical Information
Service, Springfield, Va.
Bailey, M. R., end dames, A. C. 1979. In: Biological
Implications of Radionuclides Released from Nuclear
Industries, vol. 1, pp. 465~79, International Atomic
Energy Agency, Vienna, Austria.
Bailey, M. R., Fry, F. A., andJames, A. C. 1982. The
long-term clearance kinetics of insoluble particles
from the human lung, Ann. Occup. Hyg. 26:273-
290.
Bailey, M. R., Fry, F. A., end dames, A. C. 1985a.
Long-term retention of particles in the human res-
piratory tract, J. Aerosol Sci. 16:29~305.
Bailey, M. R., Hodgson, A., and Smith, H. 1985b.
Respiratory tract retention of relatively insoluble
particles in rodents, J. Aerosol Sci. 16:279-293.
Baksi, S. N. 1982. Physiological effects of lead dusts,
In: Air Pollution- Physiological E~ects a J. McGrath
and C. D. Barnes, eds.), pp. 281-310, Academic
Press, New York.
Bang, B. G., Mukherjee, A. L., and Bang, F. B. 1967.
Human nasal mucus flow rates, Johns Hopkins Med.
J. 121:3800.
Barnhart, M. I., Chen, S., and Puro, H. 1979. Input
of diesel engine exhaust (DEE) particles on the
structural physiology of the lung, Presented at
International Symposium on the Health Effects of
Diesel Engine Emissions, Cincinnati, Ohio (De-
cember 1979).
Barnhart, M. I., Chen, S., Salley, S. O., and Puro, H.
1981. Ultrastructure and morphometry of the alve-
olar lung of guinea pigs chronically exposed to
diesel engine exhaust: six months' experience, J.
Appl. Toxicol. 1 :88-103.
Barry, P. S. I. 1975. A comparison of concentrations
of lead in human tissues, Br. J. Ind. Med. 32:119-
139.
Baselt, R. C. 1982. Disposition of Toxic Drugs and
Chemicals in Man, Biomedical Publications, Davis,
Calif.
Battigelli, M. C., Hengstenberg, F., Mannella, R. J.,
and Thomas, A. P. 1966. Mucociliary activity,
Arch. Environ. Health 12:460~66.
Biological Disposition of Airborne Particles
Beeckmans, J. M. 1965. The deposition of aerosols in
the respiratory tract. I. Mathematical analysis and
comparison with experimental data, Can. J. Physiol.
Pharmacol. 43:157-172.
Bennett, W. D., Messina, M. S., and Smaldone,
G. C. 1985. Effect of exercise on deposition and
subsequent retention of inhaled particles, J. Appl.
Physiol. 59:1046-1054.
Bergstrom, R. 1977. Acute pulmonary toxicity of
manganese dioxide, Scand. J. Work Environ. Health 3
(Suppl 1):1~1.
gingham, E., Barkley, W., Zerwas, M., Stemmer,
K., and Taylor, P. 1972. Responses of alveolar
macrophages to metals. I. Inhalation of lead and
zinc, Arch. Environ. Health 25:406014.
Blusse van Oud Alblas, A., Mattie, H., and van
Furth, R. 1983. A quantitative evaluation of pulmo-
nary macrophage kinetics, Cell Tissue Kinet.
16:211-219.
Boecker, B. B., Hahn, F. F., Cuddihy, R. G., Snipes,
M. B., and McClellan, R. O. 1983. Is the human
nasal cavity at risk from inhaled radionuclides? In:
Proceedings of the 22nd Hanford Life Sciences Sympo-
sium: Life Span Radiation E~ects Studies in Animals,
Richland, Wash. (September 1983).
Bohning, D. E., Atkins, H. L., and Cohn, S. H. 1982.
Long-term particle clearance in man: normal and
impaired, Ann. Occup. Hyg. 26:259-271.
Booker, D. V., Chamberlain, A. C., Rundo, J.,
Muir, D. C. F., and Thomson, M. L. 1967. Elim-
ination of 5 ,um particles from the human lung,
Nature 215:30-33.
Bowden, D. H., and Adamson, I. Y. R. 1980. Role of
monocytes and interstitial cells in the generation of
alveolar macrophages. I. Kinetic studies of normal
mice, Lab. Invest. 42:511-517.
Bowden, D. H., and Adamson, I. Y. R. 1984. Path-
ways of cellular efflux and particulate clearance after
carbon instillation to the lung, J. Pathol. 143:117-
125.
Brain, J. D. 1971. The effects of increased particles on
the number of alveolar macrophages, In: Inhaled
Particles III (W. H. Walton, ed. ), vol. 1, pp.
209-223, Unwin Bros., Old Woking, England.
Brain, J. D., and Mensah, G. A. 1983. Comparative
toxicology of the respiratory tract, Am. Rev. Respir.
Dis. 128(Suppl.):S87-S90.
Brain, J. D., and Valberg, P. A. 1979. Deposition of
aerosol in the respiratory tract, Am. Rev. Respir.
Dis. 120:1325-1373.
Brain, J. D., Valberg, P. A., Gehr, P., and Bloom,
S. B. 1987. Magnetic iron dust as a probe of particle
clearance, phagocytosis, and particle cytotoxicity in
the lungs, Ann. Occup. Hyg. (in press).
Brody, A. R., and Roe, M. W. 1983. Deposition
pattern of inorganic particles at the alveolar level in
the lungs of rats and mice, Am. Rev. Respir. Dis.
128:720729.
Brody, A. R., Hill, L. H., Adkins, B., Jr., and
O'Connor, R. W. 1981. Chryostile asbestos inhala-
tion in rats: deposition pattern and reaction of
alveolar epithelium and pulmonary macrophages,
Am. Rev. Respir. Dis. 123:67~679.
Brundelet, P. J. 1965. Experimental study of the dust
OCR for page 289
Richard B. Schlesinger
clearance mechanisms of the lung, Acta Pathol.
Microbiol. Scand. 175:1-141.
Buist, A. S. 1982. Evaluation of lung function: con-
cepts of normality, In: Current Pulmonology (D. H.
Simmons, ed.), vol. 4, pp. 141-165, Wiley, New
York.
Camner, P., and Philipson, K. 1972. Tracheobron-
chial clearance in smoking-discordant twins, Arch.
Environ. Health 25:60-63.
Camner, P., Hellstrom, P. A., and Lundborg, M.
1973. Coating 5,u particles with carbon and metals
for lung clearance studies, Arch. Environ. Health
27:331-333.
Camner, P., Lundborg, M., and Hellstrom, P. A.
1974. Alveolar macrophages and 5 ,um particles
coated with different metals. In vitro studies, Arch.
Environ. Health 29:211-213.
Camner, P., Mossberg, B., Philipson, K., and
Strandberg, K. 1979. Elimination of test particles
from the human tracheobronchial tract by volun-
tary coughing, Scand. J. Respir. Dis. 60:56-62.
Camner, P., Curstedt, T., Jarstrand, C., Johannsson,
A., Robertson, B., and Wiernik, A. 1985. Rabbit
lung after inhalation of manganese chloride: a com-
parison with the effects of chlorides of nickel,
cadmium, cobalt, and copper, Environ. Res. 38:
301-309.
Casarett, L. J. 1972. The vital sacs: alveolar clearance
mechanisms in inhalation toxicology, In: Essays in
Toxicology (W. Hayes, Jr., ed.), vol. 3, pp. 1-35,
Academic Press, New York.
Castranova, V., Bowman, L., Reasor, M. J., and
Miles, P. R. 1980. Effects of metallic ions on cellular
and subcellular properties of rat alveolar macro-
phages, In: Pulmonary Toxicology of Respirable Parti-
cles (C. L. Sanders, F. T. Cross, G. E. Dagle, and
J. A. Mahaffey, eds.), pp. 266-278, National Tech-
nical Information Service, Springfield, Va.
Castranova, V., Bowman, L., Reasor, M. J., Lewis,
T., Tucker, J., and Miles, P. R. 1985. The response
of rat alveolar macrophages to chronic inhalation of
coal dust and/or diesel exhaust, Environ. Res. 36:
405-419.
Chan, T. L., and Lippmann, M. 1980. Experimental
measurements and empirical modeling of the re-
gional deposition of inhaled particles in humans,
Am. Ind. Hyg. Assoc.J. 41:399 109.
Chan, T. L., Lee, P. S., Hering, W. E. 1981. Depo-
sition and clearance of inhaled diesel exhaust parti-
cles in the respiratory tract of Fischer rats, J. Appl.
Toxicol. 1:77-82.
Chan, T. L., Lee, P. S., Hering, W. E. 1984. Pulmo-
nary retention of inhaled diesel particles after pro-
longed exposure to diesel exhaust, Fundam. Appl.
Toxicol. 4:62~631.
Charles, J. M., Anderson, W. G., Menzel, D. B.
1977. Sulfate absorption from the airways of the
isolated perfused lung, Toxicol. Appl. Pharmacol.
41 :91-99.
Chen, S., Weller, M. A., and Barnhart, M. I. 1980a.
Effects of Diesel Engine Exhaust on Pulmonary
Alveolar Macrophages, GM Contract Publ. CR80-
6/BI, General Motors Corp., Detroit, Mich.
Chen, S., Weller, M. A., and Barnhart, M. I. 1980b.
289
Effects of diesel engine exhaust on pulmonary alve-
olar macrophages, Scan. Electron Microsc. 3:327-338.
Cohen, B. S., Harley, N. H., Schlesinger, R. B., and
Lippmann, M. 1987. Nonuniform particle deposi-
tion on tracheobronchial airways: implication for
lung dosimetry, Ann. Occup. Hyg. (in press).
Cohen, D. 1973. Ferromagnetic contamination in the
lungs and other organs of the human body, Science
180:745-748.
Cohen, D., Arai, S. F., and Brain, J. D. 1979.
Smoking impairs long-term dust clearance from the
lung, Science 204:514-517.
Corry, D., Kulkarni, P., and Lipscomb, M. F. 1984.
The migration of bronchoalveolar macrophages
into hilar lymph nodes, Am.J. Pathol. 115:321-328.
Craig, D. K., and Buschbom, R. L. 1975. The
alveolar deposition of inhaled plutonium aerosols in
rodents, Am. Ind. Hyg. Assoc. J. 36:172-180.
Crapo, J. D., Young, S. L., Fram, E. K., Pinkerton,
K. E., Barry, B. E., and Crapo, R. O. 1983.
Morphometric characteristics of cells in the alveolar
region of mammalian lungs, Am. Rev. Respir. Dis.
128(Suppl.):S42-S46.
Crawford, D. J. 1982. Identifying critical human
subpopulations by age groups: radioactivity and the
lung, Phys. Med. Biol. 27:539-552.
Cresia, D. A., Nettesheim, P., and Hammons, A. S.
1973. Impairment of deep lung clearance by influ-
enza virus infection, Arch. Environ. Health 26:
197-201.
Cuddihy, R. G. 1984. Mathematical models for pre-
dicting clearance of inhaled radioactive materials,
In: Lung Modellingfor Inhalation of Radioactive Mate-
rials (H. Smith and G. Gerber, eds.), pp. 167-175,
Commission of the European Communities, Lux-
embourg.
Cuddihy, R. G., Brownstein, D. G., Raabe, O. F.,
and Kanapilly, G. M. 1973. Respiratory tract dep-
osition of inhaled polydisperse aerosols in beagle
dogs, J. Aerosol Sci. 4:3~45.
Cuddihy, R. G., Boecker, B. B., and Griff~th, W. C.
1979. Modelling the deposition and clearance of
inhaled radionuclides, In: Biological Implications of
Radionuclides Releasedfrom Nuclear Industries, vol. II,
pp. 77-89, International Atomic Energy Agency,
Vienna, Austria.
Dahl, A. R., and Griff~th, W. C. 1983. Deposition of
sulfuric acid mist in the respiratory tracts of guinea
pigs and rats, J. Toxicol. Environ. Health 12:371-
383.
Dahl, A. R., Felicetti, S. A., and Muggenburg, B. A.
1983. Clearance of sulfuric acid-introduced 35S
from the respiratory tracts of rats, guinea pigs, and
dogs following inhalation or instillation, Fundam.
Appl. Toxicol. 3:293-297.
Damon, E. G., Mokler, B. V., andJones, R. K. 1983.
Influence of elastase-induced emphysema and the
inhalation of an irritant aerosol on deposition and
retention of an inhaled insoluble aerosol in Fischer-
344 rats, Toxicol. Appl. Pharmacol. 67:322-330.
Dekker, E. 1961. Transition between laminar and
turbulent flow in human trachea, J. Appl. Physiol.
16:106~1064.
DeVries, C. R., Ingram, P., Walker, S. R., Linton,
OCR for page 290
290
R. W., Gutknecht, W. F., and Shelburne, J. D.
1983. Acute toxicity of lead particulates on pulmo-
nary alveolar macrophages. Ultrastructural and micro
analytical studies, Lab. Invest. 48:3~44.
Diu, C. K., and Yu, C. P. 1983. Respiratory tract
deposition of polydisperse aerosols in humans, Am.
Ind. Hyg. Assoc. J. 44:62-65.
Driscoll, K. E., Vollmuth, T. A., and Schlesinger,
R. B. 1986. Early alveolar clearance of particles in
rabbits undergoing acute and subchronic exposure
to ozone, Fundam. Appl. Toxicol. 7:264-271.
Drown, D. B., Oberg, S. G., and Sharma, R. P. 1986.
Pulmonary clearance of soluble and insoluble forms
of manganese, J. Toxicol. Environ. Health 17:201-
212.
Dziedzic, D. 1981. Differential counts of B and T
lymphocytes in the lymph nodes, circulating blood,
and spleen after inhalation of high concentrations of
diesel exhaust, J. Appl. Toxicol. 1:111-114.
Egan, M. J., and Nixon, W. 1985. A model of aerosol
deposition in the lung for use in inhaled dose
assessments, Radiat. Protect. Dosim. 11:~17.
Esposito, A. L., and Pennington, J. E. 1983. Effects of
aging on antibacterial mechanisms in experimental
pneumonia, Am. Rev. Respir. Dis. 128:662-667.
Fairchild, G. A., Kane, P., Adams, B., and Coffin, D.
1975. Sulfuric acid and streptococci clearance from
respiratory tract of mice, Arch. Environ. Health
30:538-545.
Felicetti, S. A., Wolff, R. K., and Muggenburg, B. A.
1981. Comparison of tracheal mucous transport in
rats, guinea pigs, rabbits, and dogs,J. Appl. Physiol.
51:1612-1617.
Ferin, J. 1976. Lung clearance of particles, In: Air
Pollution and the Lung (C. F. Aharonson, A. Ben-
Davis, and M. A. Klingberg, eds.), pp. 64-78, John
Wiley and Sons, New York.
Ferin, J. 1977. Effects of particle content of lung on
clearance pathways, In: Pulmonary Macrophage and
Epithelial Cells (C. L. Sanders, R. P. Schneider,
G. E. Dagle, and H. A. Ragan, eds.), pp. 411 123,
National Technical Information Service, Spring-
field, Va.
Ferin, J., and Feldstein, M. L. 1978. Pulmonary
clearance and hilar lymph node content in rats after
particle exposure, Environ. Res. 16:342-352.
Ferin, J., and Leach, L. J. 1977. The effects of selected
air pollutants on clearance of titanic oxide particles
from the lungs of rats, In: Inhaled Particles I V (W. H.
Walton, ed.), pt. 1, pp. 333-340, Pergamon Press,
Oxford, England.
Ferron, G. A. 1977. The size of soluble aerosol
particles as a function of the humidity of the air
application to the human respiratory tract, J. Aerosol
Sci. 8:251-267.
Ferron, G. A., Kreyling, W. G., and Haider, B. 1987.
Influence of the growth of salt aerosol particles on
the deposition in the lung, Ann. Occup. Hyg. (in
press).
Findeisen, W. 1935. Uber das Absetzen Kleiner in der
Luft suspendierten Teilchen in der menschlichen
lung bei der Atmung, Arch. Ges. Physiol. 236:367-
379.
Fleischer, M., Sarofim, A. F., Fassett, D. W. Ham
Biological Disposition of Airborne Particles
mond, P., Shacklette, H. T., Nisbet, I. C. T., and
Epstein, S. 1974. Environmental impact of cad-
mium: a review by the panel on hazardous trace
substances, Environ. Health Perspect. 7:253-323.
Foord, H., Black, A., and Walsh, M. 1977. Pulmo-
nary deposition of inhaled particles with diameters
in the range of 2.5 to 7.5 ,um, In: Inhaled Particles IV
(W. H. Walton, ed.), pt. 1, pp. 137-149, Pergamon
Press, Oxford, England.
Foster, W. M., Langenbach, E., and Bergofsky, E. H.
1980. Measurement oftracheal and bronchial mucus
velocities in man: relation to lung clearance,J. Appl.
Physiol. 48:96~971.
Fowler, R. W. 1985. Aging and lung function, Age
Ageing 14:209-215.
Freedman, A. P., Robinson, S. E., and Green,
F. Y. H. 1982. Magnetopneumography as a tool for
the study of dust retention in the lungs, Ann. Occup.
Hyg. 26:319-335.
Friberg, L. 1950. Health hazards in the manufacture of
alkaline accumulators, with special reference to
chronic cadmium poisoning, Acta Med. Scand.
138(Suppl.):240.
Friberg, L., Piscator, M., Nordberg, G. F., and
Kjellstrom, T. 1974. Cadmium in the Environment,
CRC Press, Cleveland, Ohio.
Fry, F. A., and Black, A. 1973. Regional particle
deposition and clearance of particles in the human
nose,J. Aerosol Sci. 4:113-124.
Fuchs, N. A., and Sutugin, A. G. 1966. Generation
and use of monodisperse aerosols, In: Aerosol Science
(C. N. Davies, ed.), Academic Press, New York.
Gardner, D. E. 1984. Alterations in macrophage func-
tions by environmental chemicals, Environ. Health
Perspect. 55:343-358.
Gardner, N. D., Lim, S. T. K., and Lawton, J. W. M.
1981. Monocyte function in ageing humans, Mech.
Ageing Dev. 16:233-239.
Garg, B. D. 1985. Morphoquantitative analysis of
pleural surface macrophage aggregates in the lungs
of rats after a long term, low concentration expo-
sure to diesel exhaust, Presented at Annual Meeting
of American Association for Aerosol Research, Al-
buquerque, N. Mex. (November 1985).
Gehr, P. 1984. Lung morphometry, In: Lung Model-
ling for Inhalation of Radioactive Materials (H. Smith
and G. Gerber, eds.), pp. 1-11, Commission of the
European Communities, Luxembourg.
Gehr, P., Mwangi, D. K., Ammann, A., Maloiy,
G. M. O., Taylor, C. R., and Weibel, E. R. 1981.
Design of the mammalian respiratory system. V.
Scaling morphometric pulmonary diffusing capac-
ity to body mass: wild and domestic animals,
Respir. Physiol. 44:61-86.
George, A. C., and Breslin, A. J. 1967. Deposition of
natural radon daughters in human subjects, Health
Phys. 13:375-378.
Gerrard, C. S., Gerrity, T. R., and Yeates, D. B.
1986. The relationships of aerosol deposition, lung
size, and the rate of mucociliary clearance, Arch.
Environ. Health 41:11-15.
Giacomelli-Maltoni, G., Melandri, C., Prodi, V., and
Tarrone, G. 1972. Deposition eff~ciency of mono
OCR for page 291
Richard B. Schlesinger
291
disperse particles in human respiratory tract, Am.
Ind. Hyg. Assoc. J. 33:603~10.
Gibb, F. R., and Morrow, P. E. 1962. Alveolar
clearance in dogs after inhalation of an iron-59 oxide
aerosol, J. Appl. Physiol. 17:42~432.
Godard, P., Chaintreuil, J., Damon, M., Coupe, M.,
Flandre, O., de Paulet, A. C., and Michel, F. B.
1982. Functional assessment of alveolar macro-
phages: comparison of cells from asthmatic and
normal subjects, J. Allergy Clin. Immunol. 70:8~93.
Goodman, R. M., Yergin, B. M., Landa, J. F.,
Golinvaux, M. H., and Sackner, M. A. 1978.
Relationship of smoking history and pulmonary
function tests to tracheal mucus velocity in non-
smokers, young smokers, ax-smokers and patients
with chronic bronchitis, Am. Rev. Respir. Dis.
117:205-214.
Gooya, A., and Patra, A. 1986. Deposition of particles
in a baboon nose cast, Presented at 39th Annual
Conference on Engineering in Medicine and Biol-
ogy Meeting, Baltimore, Md. (September 1986).
Gore, D. J., and Patrick, G. 1982. A quantitative
study of the penetration of insoluble particles into
the tissue of the conducting airways, Ann. Occup.
Hyg. 26:149-161.
Goyer, R. A., and Chisolm, J. J. 1972. Lead, In:
Metallic Contaminants and Human Health, pp. 57-95,
Academic Press, New York.
Graham, J. A., Gardner, D. E., Waters, M. D., and
Coffin, D. L. 1975. Effect of trace metals on phago-
cytosis by alveolar macrophages, Infect. Immun. 11:
1278-1283.
Green, G. M. 1973. Alveolobronchiolar transport
mechanisms, Arch. Intern. Med. 131:109-114.
Greenspan, B. J., and Morrow, P. E. 1984. The effects
of in vitro and aerosol exposures to cadmium on
phagocytosis by rat pulmonary macrophages, Fun-
dam. Appl. Toxicol. 4:48-57.
Griff~s, L. C., Wolff, R. K., Henderson, R. F.,
Griffith, W. C., Mokler, B. V., and McClellan,
R. O. 1983. Clearance of diesel soot particles from
rat lung after a subchronic diesel exhaust exposure,
Fundam. Appl. Toxicol. 3:99-103.
Griffith, W. C., Cuddihy, R. C., Boecker, B. B.,
Guilmette, R. A., Medinsky, M. A., and Mewhin-
ney, J. A. 1983. Comparison of solubility of aero-
sols in lungs of laboratory animals, Health Phys.
45:233 (abstr.).
Gross, S. B., Pfitzer, E. A., Yeager, D. W., and
Kehoe, R. A. 1975. Lead in human tissues, Toxicol.
Appl. Pharmacol. 32:638~51.
Guyton, A. C. 1947. Measurement of the respiratory
volumes of laboratory animals, Am. J. Physiol.
150:70-77.
Hahn, F. F., and Hobbs, C. H. 1979. The effect of
enzyme-induced pulmonary emphysema in Syrian
hamsters on the deposition and long-term retention
of inhaled particles, Arch. Environ. Health 34:203-
211.
Harmsen, A. G., Muggeslburg, B. A., Snipes, M. B.,
and Bice, D. E. 1985. The role of macrophages in
particle translocation from lungs to lymph nodes,
Science 230:1277-1280.
Heinrich, V., Peters, L., Funcke, W., Pott, F., Mohr,
W., and Stober, W. 1981. Investigations of toxic
and carcinogenic effects of diesel exhaust in long-
term inhalation exposures of rodents. Presented at
U. S. Environmental Protection Agency Diesel
tm~ss~on ~ympos~um, Raleigh, N. C. (October
1981).
Henderson, R. F., Wolff, R. K., Mauderly, J. L., and
McClellan, R. O. 1982. Accumulation of diesel soot
in lungs of rodents exposed in life span studies to
diluted diesel exhaust, In: Inhalation Toxicology Re-
search Institute Annual Report 1981-1982, Lovelace
Biomedical and Environmental Research Institute,
Albuquerque, N.Mex., LMF-102, National Tech-
nical Information Service, Springf~eld, Va.
Henshaw, D. L., and Fews, A. P. 1984. The micro-
distribution of alpha emitting particles in the human
lung, In: Lung Modelling for Inhalation of Radioactive
Materials (H. Smith and G. Gerber, eds. ), pp.
199-208, Commission of the European Communi-
ties, Luxembourg.
Heppleston, A. G. 1953. Pathological anatomy of
simple pneumoconiosis in coal workers, J. Pathol.
Bacteriol. 66:235-246.
Heppleston, A. G. 1963. Deposition and disposal of
inhaled dust, Arch. Environ. Health 7:548-555.
Heyder, J., and Rudolf, G. 1977. Deposition of aero-
sol particles in the human nose, In: Inhaled Particles
IV (W. H. Walton, ed.), pt. 1, pp. 107-125, Perga-
mon Press, Oxford, England.
Heyder, J., Gebhart, J., Heigwer, G., Roth, C., and
Stahlhofen, W. 1973. Experimental studies of the
total deposition of aerosol particles in the human
respiratory tract, J. Aerosol Sci. 4: 191-208.
Heyder, J., Armbruster, L., Gebhart, J., Grein, E.,
and Stahlhofen, W. 1975. Total deposition of aero-
sol particles in the human respiratory tract for nose
and mouth breathing, J. Aerosol Sci. 6:311-328.
Heyder, J., Gebhart, J., Rudolf, G., and Stahlhofen,
W. 1980a. Physical factors determining particle
deposition in the human respiratory tract, J. Aerosol
Sci. 11 :505-515.
Heyder, J., Gebhart, J., and Stahlhofen, W. 1980b.
Inhalation of aerosols: particle deposition and reten-
tion, In: Generation ofAerosols (K. Willeke, ed.), pp.
65-103, Ann Arbor Science Publishers, Ann Arbor,
Mich.
Heyder, J., Gebhart, J., Stahlhofen, W., and Stuck, B.
1982. Biological variability of particle deposition in
the human respiratory tract during controlled and
spontaneous mouth breathing, Ann. Occup. Hyg.
26:137-147.
Hilding, A. C. 1957. Ciliary streaming in the bron-
chial tree and the time element in carcinogenesis,
N. Engl. J. Med. 256:630640.
Hilding, A. C. 1963. Phagocytosis, mucus flow and
ciliary action, Arch. Environ. Health 6:61-71.
Hinds, W. C. 1982. Aerosol Technology, Wiley Inter-
science, New York.
Hofmann, W. 1982. Mathematical model for the
postnatal growth of the human lung, Respir. Phys-
iol. 49:11~129.
Holland, J., Milic-Emili, J., Macklem, P. T., and
Bates, D. V. 1968. Regional distribution of pulmo
OCR for page 292
292
nary ventilation and perfusion in elderly subjects, J.
Clin. Invest. 47:81-92.
Holma, B. 1969. Scanning electron microscopic ob-
servation of particles depositing in the lung, Arch.
Environ. Health 18:330-339.
Holt, P. F. 1981. Transport of inhaled dust to extra-
pulmonary sites, J. Pathol . 133:123-129.
Horsfield, K., and Cumming, G. 1968. Morphology
of the bronchial tree in man, J. Appl. Physiol. 24:
373-383.
Horsfield, K., Dart, G., Olson, D. E., Filley, G., and
Cumming, G. 1971. Models of the human bron-
chial tree,J. Appl. Physiol. 31:207-217.
Hounam, R. F., Black, A., and Walsh, M. 1969.
Deposition of aerosol particles in the nasopha-
ryngeal region of the human respiratory tract, Na-
ture 221: 12501255.
Hourihane, D. O. B. 1965. A biopsy series of meso-
theliomata and attempts to identify asbestos with
some of the tumors, Ann. N. Y. Acad. Sci. 132:647-
673.
Huhnerbein, J., Otto, J., and Thal, W. 1984. Unter-
suchungsergebnisse der mukoziliaren Clearance bei
lungengesunden Kindern, Padiat. Grenzgeb. 23:
437 443.
International Commission on Radiation Protection.
1959. Report of Committee II on Permissible Dose for
Internal Radiation, Publ. 2, Pergamon Press, Ox-
ford, England.
International Commission on Radiation Protection.
1972. The Metabolism of Compounds of Plutonium and
Other Actinides, Publ. 19, Pergamon Press, Oxford,
England.
Itoh, H., Smaldone, G. C., Swift, D. L., and Wagner,
H. N. 1985. Mechanisms of aerosol deposition in a
nasal model, J. Aerosol Sci. 16:529-534.
Jammet, H., Drutel, P., Parrot, R., and Roy, M.
1978. Etude de l'epuration pulmonaire chez
l'homme apres administration d'aerosols de parti-
cules radioactives, Radioprotection 13:143-166.
Johnson, R. F., Jr., and Zeimer, P. L. 1971. The
deposition and retention of inhaled ~52~~54europium
oxide in the rat, Health Phys. 20:187-193.
Kanapilly, G. M., Wolff, R. K., DeNee, P. B., and
McClellan, R. O. 1982. Generation, characteriza-
tion and inhalation deposition of ultrafine aggregate
aerosols, Ann. Occup. Hyg. 26:77-91.
Kehoe, R. A. 1961. The metabolism of lead in man in
health and disease: the metabolism of lead under
abnormal conditions, J. Roy. Inst. Public Health
Hyg. 24:101-120.
Kilburn, K. H. 1968. A hypothesis for pulmonary
clearance and its implications, Am. Rev. Respir. Dis.
98:449063.
Kliment, V. 1973. Similarity and dimensional analysis
evaluation of aerosol deposition in the lungs of
laboratory animals and man, Folia Morphol. 21:
59-66.
Kliment, V. 1974. Dichotomical model of respiratory
airways of the rabbit and its significance for the
construction of deposition models, Folia Morphol.
22:286-290.
Kliment, V., Libich, J., and Kaudersova, V. 1972.
Geometry of guinea pig respiratory tract and appli
Biological Disposition of Airborne Particles
cation of Landahls' model of deposition of aerosol
particles, J. Hyg. Epidemiol. Microbiol. Immunol.
16:107-114.
Lakin, M. B., and Fox, V. G. 1974. Transient flow
characteristics in an idealized bronchial bifurcation,
Respir. Physiol. 21:101-117.
Landahl, H. D., Tracewell, T. N., and Lassen, W. H.
1951. On the retention of airborne particulates in
the human lung, Arch. Ind. Hyg. Occup. Med. 3:
350366.
Landahl, H. D., Tracewell, T. N., and Lassen, W. H.
1952. Retention of airborne particulates in the hu-
man lung, III, Arch. Ind. Hyg. Occup. Med. 6:508-
511.
Lauweryns, J. M., and Baert, J. H. 1974. The role of
the pulmonary lymphatics in the defenses of the
distal lung: morphological and experimental studies
of the transport mechanisms of intratracheally in-
stilled particles, Ann. N.Y. Acad. Sci. 221:241 275.
Leak, L. V. 1980. Lymphatic removal of fluids and
particles in the mammalian lung, Environ. Health
Perspect. 35:5~76.
Lee, K. P., Barras, C. E., Griffith, F. D., and Waritz,
R. S. 1981. Pulmonary response and transmigration
of organic fibers by inhalation exposure, Am. J.
Pathol. 102:310322.
Lee, P. S. 1981. Clearance of inhaled titanium dioxide
dust in the control of diesel exposed rats, Presented
at Twentieth Annual Meeting of Society of Toxi-
cology, San Diego, Calif. (March 1981).
Lee, P. S., Gerrity, T. R., Hass, F. T., and Lourenco,
R. V. 1979. A model for tracheobronchial clearance
of inhaled particles in man and a comparison with
the data, IEEE Trans. Biomed. Eng. 26:62~630.
Lee, P. S., Chan, T. L., and Hering, W. E. 1983.
Long-term clearance of inhaled diesel exhaust par-
ticles in rodents, J. Toxicol. Environ. Health 12:
801-813.
Lee, R. E., Jr., and van Lehmden, D. J. 1973. Trace
metal pollution in the environment, J. Air Pollut.
Control Assoc. 23:85~857.
LeFevre, M. E., Green, F. H. Y., Joel, D. D., and
Laqueur, W. 1982. Frequency of black pigment in
livers and spleens of coal workers. Correlation with
pulmonary pathology and occupational informa-
tion, Human Pathol. 13:1121-1132.
Lehnert, B. E., and Morrow, P. E. 1985. Association
of 59iron oxide with alveolar macrophages during
alveolar clearance, Exp. Lung Res. 9:1-16.
Lehnert, B. E., Valdez, Y. E., and Stewart, C. C.
1986. Translocation of particles to the tracheobron-
chial lymph nodes after lung deposition: kinetics
and particle-cell relationships, Exp. Lung Res.
10:24~266.
Lehnert, B. E., Valdez, Y. E., and Hyler, S. 1987.
Translocation of particles to the pleural space and
hilar lymph nodes, and the distribution of particles
in the lung free cells following their deposition in
the lung, Ann. Occup. Hyg. (in press).
Leikauf, G., Yeates, D. B., Wales, K. A., Albert,
R. E., and Lippmann, M. 1981. Effects of sulfuric
acid aerosol on respiratory mechanics and mucocil-
iary particle clearance in healthy nonsmoking
adults, Am. Ind. Hyg. Assoc. J. 42:27~282.
OCR for page 293
Richard B. Schlesinger
293
Leikauf, G. D., Spektor, D. M., Albert, R. E., and
Lippmann, M. 1984. Dose-dependent effects of
submicrometer sulfuric acid aerosol on particle
clearance from ciliated human lung airways, Am.
Ind. Hyg. Assoc. J. 45:285-292.
Leith, D. E. 1983. Comparative mammalian respira-
tory mechanics, Am. Rev. Respir. Dis. 128(Suppl.):
S77-S82.
Lippmann, M. 1970. Deposition and clearance of
inhaled particles in the human nose, Ann. Otol.
Rhinol. Laryugol. 79:1-10.
Lippmann, M. 1977. Regional deposition of particles
in the human respiratory tract, In: Handbook of
Physiology, Reactions to Environmental Agents (D. H.
K. Lee, H. L. Falk, and S. D. Murphy, eds.), vol. 9,
pp. 213-232, American Physiological Society, Be-
thesda, Md.
Lippmann, M., and Albert, R. E. 1969. The effect of
particle size on the regional deposition of inhaled
aerosols in the human respiratory tract, Am. Ind.
Hyg. Assoc. J. 30:257-275.
Lippmann, M., and Altshuler, B. 1976. Regional
deposition of aerosols, In: Air Pollution and the Lung
(E. F. Aharonson, A. Ben-David, and M. A. Kling-
berg, eds.), pp. 25~8, Wiley, New York.
Lippmann, M., and Schlesinger, R. B. 1984. Interspe-
cies comparison of particle deposition and mucocil-
iary clearance in tracheobronchial airways, J. Toxi-
col. Environ. Health 13:441-469.
Lippmann, M., Albert, R. E., and Peterson, H. T., Jr.
1972. The regional deposition of inhaled aerosols in
man, In: Inhaled Particles III (W. H. Walton, ed.),
pp. 105-120, Unwin Bros., Surrey, England.
Lippmann, M., Yeates, D. B., and Albert, R. E. 1980.
Deposition, retention and clearance of inhaled par-
ticles, Br. J. Ind. Med. 37:337-362.
Lourenco, R. V., Klimek, M. F., and Borowski, C. J.
1971a. Deposition and clearance of 2 ,u particles in
the tracheobronchial tree of normal subjects
smokers and non-smokers, J. Clin. Invest. 50:1411-
1420.
Lourenco, R. V., Stanley, E. D., Gatmaitan, B., and
Jackson, G. G. 1971b. Abnormal deposition and
clearance of inhaled particles during upper respira-
tory and viral infections, J. Clin. Invest. 50:62a.
Lourenco, R. V., Loddenkemper, R., and Cargan,
R. W. 1972. Patterns of distribution and clearance
of aerosols in patients with bronchiectasis, Am. Rev.
Respir. Dis. 106:857-866.
Love, R. G., Muir, D. C. F., and Sweetland, K. F.
1971. Aerosol deposition in the lungs of coalwork-
ers, In: Inhaled Particles III (W. H. Walton, ed.), vol.
I, pp. 131-139, Unwin Bros., Surrey, England.
Lucas, A. M., and Douglas, L. C. 1934. Principles
underlying ciliary activity in the respiratory tract.
II. A comparison of nasal clearance in man, monkey
and other mammals, Arch. Otolaryugol. 20:518-541.
Luckey, T. D., and Venugopal, B. 1977. Metal Tox-
icity in Mammals. 1. Physiological and Chemical Basis
for Metal Toxicity, Plenum Press, New York.
Lundborg, M., Lind, B., and Camner, P. 1984.
Ability of rabbit alveolar macrophages to dissolve
metals, Exp. Lung Res. 7:11-22.
Lundborg, M., Eklund, A., Lind, B., and Camner, P.
1985. Dissolution of metals by human and rabbit
alveolar macrophages, Br. J. Ind. Med. 42:642-645.
Macklin, C. C. 1955. Pulmonary sumps, dust accu-
mulation, alveolar fluid and lymph vessels, Acta
Anat. 23:1-21.
Mahoney, J. P., and Small, W. J. 1968. Studies on
manganese. III. The biological half-life of radio-
manganese in man and factors which affect this
half-life, J. Clin. Invest. 47:643-653.
Maigetter, R. Z., Ehrlich, R., Fenters, J. D., and
Gardner, D. E. 1976. Potentiating effects of man-
ganese dioxide on experimental respiratory infec-
tions, Environ. Res. 11 :38~391.
Majima, Y., Sakakura, Y., Matsubara, T., Murai, S.,
and Miyoshi, Y. 1983. Mucociliary clearance in
chronic sinusitis: related human nasal clearance and
in vitro bullfrog palate clearance, Biorheology
20:251-262.
Man, S. F. P., Lee, T. K., Gibney, R. T. N., Logus,
J. W., and Noujaim, A. A. 1980. Canine tracheal
mucus transport of particulate pollutants: compari-
son of radiolabeled corn pollen, ragweed pollen,
asbestos, silica, and talc to Dowex~ anion exchange
particles, Arch. Environ. Health 35:283-286.
Manton, W. I. 1977. Sources of lead in blood: identi-
fication by stable isotopes, Arch. Environ. Health
32:149-159.
Martens, A., andJacobi, W. 1974. Die in vivo Bestim-
mung der Aerosolteilchendeposition in Atemtrakt
bei Mund-bzur. Nasenatmung, In: Aerosols in Phy-
sik, Medizin und Technik, pp. 117-121, Gesellschaft
fur Aerosolforschung, Bad Soden.
Martonen, T. B. 1985. The effect of age on reg~onal
aerosol deposition in man, Presented at Annual
Meeting of American Association for Aerosol Re-
search, Albuquerque, N.Mex. (November 1985).
Martonen, T., and Gibby, D. 1982. Computer mod-
els of aerosol deposition in two human tracheo-
bronchial geometries, Comp. Biomed. Res. 15:42
433.
Martonen, T. B., and Patel, M. 1981. Computation of
ammonium bisulfate aerosol deposition in conduct-
ing airways, J. Toxicol. Environ. Health 8:1001-
1014.
Masse, R. 1971. Etude cytologique comparee de l'in-
fluence du plutonium et de la silica inhales sur le
comportement du macrophage alveolaire, In: In-
haled Particles III (W. H. Walton, ed.), vol. 1, pp.
247-257, Unwin Bros., Surrey, England.
Masse, R., Ducousso, R., Nolibe, D., LaEuma, J., and
Chretien, J. 1974. Passage transbronchique des par-
ticules metalliques, Rev. Fr. Mal. Respir. 1:123-129.
Matthys, H., Vastag, E., Kohler, D., Daikeler, G.,
and Fischer, J. 1983. Mucociliary clearance in pa-
tients with chronic bronchitis and bronchial carci-
noma, Respiration 44:329-337.
Mauderly, J. L. 1979. Effect of age on pulmonary
structure and function of immature and adult ani-
mals and man, Fed. Proc. 38:173-177.
Mauderly, J. L., Jones, R. K., Henderson, R. F.,
Wolff, R. K., Pickrell, J. A., McClellan, R. O., and
Gillett, N. A. 1987. Relationship of lung structural
and functional changes to accumulation of diesel
exhaust particles, Ann. Occup. Hyg. (in press).
OCR for page 294
294
McMahon, T. A., Brain, J. D., and LeMott, S. R.
1977. Species difference in aerosol deposition, In:
Inhaled Particles IV (W. H. Walton, ed.), pt. 1, pp.
23-33, Pergamon Press, Oxford, England.
Meessen, H. 1960. Die pathomorphologic der Diffu-
sion und Perfusion, Verh. Dtsch. Ges. Pathol. 44:98-
106.
Mercer, T. T. 1967. On the role of particle size in the
dissolution of lung burdens, Health Phys. 13:1211-
1221.
Mercer, T. T. 1975. The deposition model of the Task
Group on Lung Dynamics: a comparison with
recent experimental data, Health Phys. 29:673-680.
Metivier, H. 1984. Animal data on clearance, In: Lung
Modelling for Inhalation of Radioactive Materials (H.
Smith and G. Gerber, eds.), pp. 77-89, Commis-
sion of the European Communities, Luxembourg.
Moore, M. R., Meredith, P. A., and Goldberg, A.
1980. Lead and heme biosynthesis, In: Lead Toxicity
(R. L. Singhal and J. A. Thomas, eds.), pp. 79-117,
Urban and Schwarzenberg, Munich.
Moore, W., Orthoefer, J. G., Burkart, J. K., and
Malanchuk, M. 1978. Preliminary findings on the
deposition and retention of automotive diesel par-
ticulate in rat lungs, In: Proceedings of the 71st Annual
Meeting of the Air Pollution Control Association, Hous-
ton, Tex. (June 1978).
Moores, S. R., Black, A., Lambert, B. E., Lindop,
P. J., Morgan, A., Pritchard, J., and Walsh, M.
1980. Deposition of thorium and plutonium oxides
in the respiratory tract of the mouse, In: Pulmonary
Toxicology of Respirable Particles (C. L. Sanders,
F. T. Cross, G. E. Dagle, andJ. A. Mahaffey, eds.),
pp. 103-118. National Technical Information Ser-
vice, Springfield, Va.
Morgan, A., and Holmes, A. 1980. Concentrations
and dimensions of coated and uncoated asbestos
fibers in the human lung, Br. J. Ind. Med. 37:2~32.
Morgan, W. K. C., Ahmad, D., Chamberlain, M. J.,
Clague, H. W., Pearson, M. G., and Vinitski, S.
1984. The effect of exercise on the deposition of an
inhaled aerosol, Respir. Physiol. 56:327-338.
Morrow, P. E. 1973. Alveolar clearance of aerosols,
Arch. Intern. Med. 131 :101-108.
Morrow, P. E. 1977. Clearance kinetics of inhaled
particles, In: Respiratory Defense Mechanisms a D.
Brain, D. F. Proctor, and L. M. Reid, eds.), pt. II,
pp. 491-543, Marcel Dekker, New York.
Morrow, P. E. 1981. Aerosol factors affecting respi-
ratory deposition, In: Proceedings of International
Symposium on Deposition and Clearance of Aerosols in
the Human Respiratory Tract, Bad Gleichenberg,
Austria (May 1981).
Morrow, P. E., Gibb, F. R., end Johnson, L. 1964.
Clearance of insoluble dust from the lower respira-
tory tract, Health Phys. 10:543-555.
Morrow, P. E., Gibb, F. R., and Gazioglu, K. M.
1967a. The clearance of dust from the lower respi-
ratory tract of man: an experimental study, In:
Inhaled Particles and Vapours II (C. N. Davies, ed.),
pp. 351-358, Pergamon Press, London.
Morrow, P. E., Gibb, F. R., and Gazioglu, K. M.
1967b. A study of particulate clearance from the
human lung, Am. Rev. Respir. Dis. 96:120~1221.
Biological Disposition of Airborne Particles
Morrow, P. E., Beiter, H., Amato, F., and Gibb,
F. R. 1980. Pulmonary retention of lead: an exper-
imental study in man, Environ. Res. 21:373-384.
Muhle, H., Bellman, B., and Heinrich, U. 1987.
Overloading of lung clearance after chronic expo-
sure of experimental animals to particles, Ann.
Occup. Hyg. (in press).
Muir, D. C. F., and Davies, C. N. 1967. The depo-
sition of 0.5 ,um diameter aerosols in the lungs of
man, Ann. Occup. Hyg. 10:161-174.
Myron, D. R., Zimmerman, T. J., and Schuler, T. R.
1978. Intake of nickel and vanadium by humans. A
survey of selected diets, Am. J. Clin. Nutr. 31:527-
531.
Natusch, D. F. S., Wallace, J. R., and Evans, C. A., Jr.
1974. Toxic trace elements: preferential concentra-
tion in respirable particles, Science 183:202-204.
Natusch, D. F. S., Wallace, J. R., and Evans, C. A.
1975. Concentration of toxic species in submicrom-
eter size airborne particles-the lung as a preferen-
tial absorption site, Am. Inst. Chem. Eng. Symp.
Series No. 147, vol. 71.
Naumann, B. D., and Schlesinger, R. B. 1986. As-
sessment of early alveolar particle clearance and
macrophage function following an acute inhalation
of sulfuric acid mist, Exp. Lung Res. 11:13-33.
Newhouse, M. T., Dolovich, M., and Obminski, G.
1978. Effect of TLV levels of SO2 and H2SO4 on
bronchial clearance in exercising man, Arch. Envi-
ron. Health 33:24-32.
Newton, D., Fry, F. A., Taylor, B. T., Eagle, M. C.,
and Shorma, R. C. 1978. Interlaboratory compari-
son of techniques for measuring lung burdens of
low energy protein emitters, Health Phys. 35:751-
771.
Niinimaa, V., Cole, P., Mintz, S., and Shephard,
R. J. 1980. The switching point from nasal to
oronasal breathing, Respir. Physiol. 42:61-71.
Nikiforov, A. I., and Schlesinger, R. B. 1985. Mor-
phometric variability of the human upper bronchial
tree, Respir. Physiol. 59:28~299.
Nozaki, K. 1966. Method for studies on inhaled
particles in human respiratory system and retention
of lead fume, Ind. Health 4:11~122.
Oberdorster, G., and Hochrainer, D. 1980. Lung clear-
ance of Fe2O3 and CdCl2 aerosols during chronic
CdO inhalation, In: Aerosols in Science' Medicine and
Technology, Proceedings of the 8th Conference on Aero-
sol Research, Schmallenberg, Germany.
Oberdorster, G., Baumert, H.-P., Hochrainer, D.,
and Stoeber, W. 1979. The clearance of cadmium
aerosols after inhalation exposure, J. Am. Ind. Hyg.
Assoc. 40:443-450.
Oberdorster, G., Green, F. Y. H., and Freedman,
A. P. 1984. Clearance of 59Fe203 particles from the
lungs of rats during exposure to coal mine dust and
diesel exhaust, J. Aerosol Sci. 15:235-237.
Olson, D. E., Dart, G. A., and Filley, G. F. 1970.
Pressure drop and fluid flow regime of air inspired
into the human lung, J. Appl. Physiol. 28:482-494.
Olson, D. E., Sudlow, M. F., and Horsfield, K. 1973.
Convective patterns of flow during inspiration,
Arch. Intern. Med. 131 :51-57.
Palm, P. E., McNerney, J. M., and Hatch, T. 1956.
OCR for page 295
Richard B. Schlesinger
Respiratory dust retention in small animals. A com-
parison with man, Arch. Ind. Health 13:35~365.
Parker, H., Horsfield, K., and Cumming, G. 1971.
Morphology of distal airways in the human lung, J.
Appl. Physiol. 31:38~391.
Passali, D., and Ciampoli, M. B. 1985. Normal values
of mucociliary transport time in young subjects,
Int. J. Pediatr. Otorhinolaryugol. 9:151-156.
Patra, A. L. 1986. Comparative anatomy of mamma-
lian respiratory tract: the nasopharyngeal region and
the tracheobronchial tree, J. Toxicol. Environ.
Health 17:16~174.
Patrick, G., and Stirling, C. 1977. The retention of
particles in large airways of the respiratory tract,
Proc. Roy. Soc. London, Ser. V 198:455 462.
Patterson, C. C. 1965. Contaminated and natural lead
environments of man, Arch. Environ. Health 11 :34
360.
Pattle, R. E. 1961. The retention of gases and particles
in the human nose, In: Inhaled Particles and Vapours
(C. N. Davies, ed.), pp. 302-309, Pergamon Press,
Oxford, England.
Pavia, D. 1984. Lung mucociliary clearance, In: Aero-
sols and the Lung (S. W. Clarke and D. Pavia, eds.),
pp. 127-155, Butterworths, London.
Pavia, D., Bateman, J. R. M., Sheahan, N. F.,
Agnew, J. E., and Clarke, S. W. 1985. Tracheo-
bronchial mucociliary clearance in asthma: impair-
ment during remission, Thorax 40:171-175.
Phalen, R. F. 1987. Particle deposition predictions for
infants, children and adolescents, Ann. Occup. Hyg.
(in press).
Phalen, R. F., and Oldham, M. J. 1985. Predicted
particle deposition eff~ciency of the newborn's nose,
Presented at Annual Meeting of American Associ-
ation for Aerosol Research, Albuquerque, N.Mex.
(November 1985).
Phalen, R., Kenoyer, J., and Davis, J. 1977. Deposi-
tion and clearance of inhaled particles: comparison
of mammalian species, In: Proceedings of the Annual
Conference on Environmental Toxicology, vol. 7, pp.
15~170, AMRL-TR-76-125, National Technical
Information Service, Springfield, Va.
Phalen, R. F., Yeh, H. C., Schum, G. M., and Raabe,
O. G. 1978. Application of an idealized model of
morphometry of the tracheobronchial tree, Anat.
Rec. 190: 167-176.
Phalen, R. F., Kenoyer, J. L., Crocker, T. T., and
McClure, T. R. 1980. Effects of sulfate aerosols in
combination with ozone on elimination of tracer
particles inhaled by rats, J. Toxicol. Environ. Health
6:797-810.
Phalen, R. F., Oldham, M. J., Beaucage, C. B.,
Crocker, T. T., and Mortensen, J. D. 1985. Post-
natal enlargement of human tracheobronchial air-
ways and implications for particle deposition, Anat.
Rec. 212:368-380.
Philipson, K., Falk, R., and Camner, P. 1985. Long-
term lung clearance in humans studied with teflon
particles labeled with chromium-51, Exp. Lung Res.
9:31~2.
Phipps, R. J. 1981. The airway mucociliary system,
In: International Review of Physiology: Respiratory
295
Physiology a G. Widdicombe, ed.), vol. 23, pp.
21~259, University Park Press, Baltimore, Md.
Pooley, F. 1974. Locating fibers in the bowel wall,
Environ. Health Perspect. 9:235.
Pritchard,J. N.,Jane-Jefferies, S., end Black, A. 1987.
Regional deposition of 2.5 to 5.0 ,um polystyrene
microspheres inhaled by women, Ann. Occup. Hyg.
(in press).
Proctor, D. F. 1980. The upper respiratory tract, In:
Pulmonary Diseases and Disorders (A. P. Fishman,
ed.), pp. 209-223, McGraw-Hill, New York.
Puchelle, E., Zahm, J. M., Girard, F., Bertrand, A.,
Polu, J. M., Aug. F., and Sadoul, P. 1980. Muco-
ciliary transport in vivo and in vitro-relations to
sputum properties in chronic bronchitis, Eur. J.
Respir. Dis. 61:250264.
Puro, H. 1980. Light microscopic findings in lungs of
rats and guinea pigs exposed to diesel exhaust, GM
Research Laboratories Publ. CR80-7/BI, General
Motors Corp., Detroit, Mich.
Raabe, O. G. 1982. Deposition and clearance of
inhaled aerosols, In: Mechanisms in Respiratory Tox-
icology (H. Witschi and P. Nettesheim, eds.), pp.
27-76, CRC Press, Boca Raton, Fla.
Raabe, O. G., Yeh, H. C., Newton, G. J., Phalen,
R. J., and Velazquez, D. J. 1977. Deposition of
inhaled monodisperse aerosols in small rodents, In:
Inhaled Particles IV (W. H. Walton, ed.), pt. 1, pp.
~20, Pergamon Press, Oxford, England.
Raabe, O. G., Ali-Bayati, M. A., Rasolt, A., and
Teague, S. V. 1987. Regional deposition of inhaled
monodisperse coarse and fine aerosol particles in
small laboratory animals, Ann. Occup. Hyg. (in
press).
Rabinowitz, M. B., Wetherill, G. W., and Kopple,
J. D. 1973. Lead metabolism in the normal human:
stable isotope studies, Science 182:72~727.
Rabinowitz, M. B., Wetherill, G. W., and Kopple,
J. D. 1974. Studies of human lead metabolism by
use of stable isotope tracers, Environ. Health Per-
spect. 7: 14~153.
Rabinowitz, M. B., Wetherill, G. W., and Kopple,
J. D. 1976. Kinetic analysis of lead metabolism in
healthy humans, J. Clin. Invest. 58:260-270.
Radford, E. P., and Martell, E. A. 1977. Polonium-
210: lead 210 ratios as an index of residence times of
insoluble particles from cigarette smoke in bron-
chial epithelium, In: Inhaled Particles IV (W. H.
Walton, ed.), pt. 2, pp. 567-580, Pergamon Press,
Oxford, England.
Rahola, T., Aaran, R. K., and Miettinen, J. K. 1972.
Half-time studies of mercury and cadmium by
whole body counting, In: Assessment of Radioactive
Contamination in Man, International Atomic Energy
Agency, Vienna, Austria.
Robertson, B. 1980. Basic morphology of the pulmo-
nary defense system, Eur.J. Respir. Dis. 61(Suppl.
107):21~0.
Rudd, C. J., and Strom, K. A. 1981. A spectropho-
tometric method for the quantitation of diesel ex-
haust particles in guinea pig lung, J. Appl. Toxicol.
1 :8~87.
Rudolf, G., Gebhart, J., Heyder, J., Scheuch, G., and
Stahlhofen, W. 1987. Mass deposition from in
OCR for page 296
296
spired polydisperse aerosols, Ann. Occup. Hyg. (in
press).
Rutland, J., and Cole, P. J. 1981. Nasal mucociliary
clearance and ciliary beat frequency in cystic fibrosis
compared with sinusitis and bronchiectasis, Thorax
36:654 658.
Sackner, M. A., Ford, D., Fernandez, R., Cipley, J.,
Perez, D., Kwoka, M., Reinhart, M., Michaelson,
E. D., Schreck, R., and Wanner, A. 1978. Effects
of sulfuric acid aerosol on cardiopulmonary func-
tion of dogs, sheep and humans, Am. Rev. Respir.
Dis. 118:497-510.
Schiller, C. F., Gebhart, J., Heyder, J., Rudolf, G.,
and Stahlhofen, W. 1987. Deposition of monodis-
perse insoluble aerosol particles in the 0.005 to 0.2
,um size range within the human respiratory tract,
Ann. Occup. Hyg. (in press).
Schlesinger, R. B. 1985. Clearance from the respira-
tory tract, Fundam. Appl. Toxicol. 5:435050.
Schlesinger, R. B. 1986. The effects of inhaled acids on
respiratory tract defense mechanisms, Environ.
Health Perspect. 63:2~38.
Schlesinger, R. B. 1987. Functional assessment of
rabbit alveolar macrophages following intermittent
inhalation exposures to sulfuric acid mist, Fundam.
Appl. Toxicol. 8:328-334.
Schlesinger, R. B., and Gearhart, J. M. 1986. Early
alveolar clearance in rabbits intermittently exposed
to sulfuric acid mist, J. Toxicol. Environ. Health
17:21~220.
Schlesinger, R. B., and Gearhart, J. M. 1987. Inter-
mittent exposures to mixed atmospheres of nitro-
gen dioxide and sulfuric acid: effect on particle
clearance from the respiratory region of rabbit
lungs, Toxicology 44:309-319.
Schlesinger, R. B., and Lippmann, M. 1978. Selective
particle deposition and bronchogenic carcinoma,
Environ. Res. 15:421 431.
Schlesinger, R. B., and McFadden, L. 1981. Compar-
ative morphometry of the upper bronchial tree in
six mammalian species, Anat. Rec. 199:99-108.
Schlesinger, R. B., Lippmann, M., and Albert, R.
1978. Effects of short-term exposures to sulfuric
acid and ammonium sulfate aerosols upon bronchial
airway function in the donkey, Am. Ind. Hyg. Assoc.
J. 39:27~286.
Schlesinger, R. B., Halpern, M., Albert, R. E., and
Lippmann, M. 1979. Effects of chronic inhalation of
sulfuric acid mist upon mucociliary clearance from
the lungs of donkeys, J. Environ. Pathol. Toxicol.
2:1351-1367.
Schlesinger, R. B., Gurman, J. L., and Lippmann, M.
1982. Particle deposition within bronchial airways:
comparisons using constant and cyclic inspiratory
flow, Ann. Occup. Hyg. 26:47-64.
Schlesinger, R. B., Concato, J., and Lippmann, M.
1983a. Particle deposition during exhalation: a
study in replicate casts of the human upper tracheo-
bronchial tree, In: Aerosols in the Mining and Indus-
trial Work Environment (B. Liu and V. Marple, eds.),
pp. 165-176, Ann Arbor Science Publishers, Ann
Arbor, Mich.
Schlesinger, R. B., Naumann, B. D., and Chen, L. C.
1983b. Physiological and histological alterations in
Biological Disposition of Airborne Particles
the bronchial mucociliary clearance system of rab-
bits following intermittent oral or nasal inhalation
of sulfuric acid mist, J. Toxicol. Environ. Health
12:441-465.
Schlesinger, R. B., Chen, L. C., and Driscoll, K. E.
1984. Exposure-response relationship of bronchial
mucociliary clearance in rabbits following acute
inhalations of sulfuric acid mist, Toxicol. Lett.
22:249-254.
Schlesinger, R. B., Vollmuth, T. A., Naumann,
B. D., and Driscoll, K. E. 1986. Measurement of
particle clearance from the alveolar region of the
rabbit respiratory tract, Fundam. Appl. Toxicol.
7:256-263.
Schreider, J. P. 1986. Comparative anatomy and
functions of the nasal passages, In: Toxicology ofthe
Nasal Passages (C. S. Barrow, ed.), pp. 1-25, Mc-
Graw-Hill, New York.
Schreider, J. P., and Hutchens, J. O. 1979. Particle
deposition in the guinea pig respiratory tract, J.
Aerosol Sci. 10:599-607.
Schroeder, H. A., Balassa, J. J., and Tipton, I. H.
1963. Abnormal trace metals in man vanadium,J.
Chronic Dis. 16:1047-1071.
Schum, G. M., and Yeh, H. C. 1980. Theoretical
evaluation of aerosol deposition in anatomical mod-
els of mammalian lung airways, Bull. Math. Biol.
42:1-15.
Schum, G. M., Duggan, M. T., and Yeh, H. C. 1976.
Tracheobronchial anatomy: species differences in
branching patterns, In: Inhalation Toxicology Re-
search Institute Annual Report 1975-1976, Lovelace
Biomedical and Environmental Institute, Albuquer-
que, N.Mex.
Scott, W. R., Taulbee, D. B., and Yu, C. P. 1978.
Theoretical study of nasal deposition, Bull. Math.
Biol. 40:581-603.
Sekihara, T., Olson, D. E., and Filley, G. F. 1968.
Airflow regimes and geometrical factors in the
human airways, In: Current Research in Chronic
Respiratory Disease: Proceedings ofthe Eleventh Aspen
Emphysema Conference, pp. 103-114, U.S. Depart-
ment of Health, Education and Welfare, Washing-
ton, D.C.
Snipes, M. B., and Clem, M. F. 1981. Retention of
microspheres in the rat lung after intratracheal in-
stillation, Environ. Res. 24:33-41.
Snipes, M. B., Boecker, B. B., and McClellan, R. O.
1983. Retention of monodisperse or polydisperse
aluminosilicate particles inhaled by dogs, rats, and
mice, Toxicol. Appl. Pharmacol. 69:345-362.
Snipes, M. B., Boecker, B. B., and McClellan, R. O.
1984a. Respiratory tract clearance of inhaled parti-
cles in laboratory animals, In: Lung Modelling for
Inhalation of Radioactive Materials (H. Smith and G.
Gerber, eds.), pp. 63-71, Commission of the Euro-
pean Communities, Luxembourg.
Snipes, M. B., Chavez, G. T., and Muggenburg,
B. A. 1984b. Disposition of 3-, 7-, and 13-,um
microspheres instilled into lungs of dogs, Environ.
Res. 33:333-342.
Snyder, B., and Jaeger, M. J. 1983. Lobar flow
patterns in a hollow cast of canine central airways, J.
Appl. Physiol. 54:749-756.
OCR for page 297
Richard B. Schlesinger
Soong, T. T., Nicolaides, P., Yu, C. P., and Soong,
S. C. 1979. A statistical description of the human
tracheobronchial tree geometry, Respir. Physiol.
37:161-172.
Sorokin, S. P., and Brain, J. D. 1975. Pathways of
clearance in mouse lungs exposed to iron oxide
aerosols, Anat. Rec. 181:581-626.
Spell, K. E. 1969. Comparative studies in lung me-
chanics based on a survey of literature data, Respir.
Physiol. 8:37-57.
Stahl, W. R. 1967. Scaling of respiratory variables in
mammals,J. Appl. Physiol. 22:453~60.
Stahlhofen, W., Gebhart, J., and Heyder, J. 1981a.
Biological variability of regional deposition of aero-
sol particles in the human respiratory tract, Am. Ind.
Hyg. Assoc. J. 42:348-352.
Stahlhofen, W., Gebhart, J., Heyder, J., Philipson,
K., and Camner, P. 1981b. Intercomparison of
regional deposition of aerosol particles in the human
respiratory tract and their long-term elimination,
Exp. Lung Res. 2:131-139.
Stanley, P. J., MacWilliam, L., Greenstone, M. A.,
Daly, C., and Cole, P. J. 1984. Prolonged nasal
mucociliary clearance in healthy smokers, Thorax
39:239 (abstr).
Stanley, P. J., Wilson, R., Greenstone, M. A., Mac-
kay, I. S., and Cole, P. J. 1985. Abnormal nasal
mucociliary clearance in patients with rhinitis and
its relationship to concomitant chest disease, Br. J.
Dis. Chest 79:77-82.
Stauffer, D. 1975. Scaling theory for aerosol deposi-
tion in the lungs of different mammals, J. Aerosol
Sci. 6:223-225.
Strom, K. A. 1984. Response of pulmonary cellular
defenses to the inhalation of high concentrations of
diesel exhaust, J. Toxicol. Environ. Health 13:919-
944.
Sunderman, F. W., Jr., 1977. A review of the metab-
olism and toxicology of nickel, Ann. Clin. Lab. Sci.
7:377-398.
Sweeney, T. D., Brain, 3. D., Tryka, A. F., and
Godleski, J. J. 1983. Retention of inhaled particles in
hamsters with pulmonary fibrosis, Am. Rev. Respir.
Dis. 128:138-143.
Swift, D. L. 1981. Aerosol deposition and clearance in
the human upper airways, Ann. Biomed. Engl.
9:593-604.
Swift, D. L., and Proctor, D. F. 1977. Access of air to
the respiratory tract, In: Respiratory Defense Mecha-
nisms a D. Brain, D. F. Proctor, and L. M. Reid,
eds.), pt. 1, pp. 63-93, Marcel Dekker, New York.
Swift, D. L., and Proctor, D. F. 1987. A dosimetric
model for particles in the respiratory tract above the
trachea, Ann. Occup. Hyg. (in press).
Swift, D. L., Cobb, J. A. C., and Smith, J. C. 1977a.
Aerosol deposition in the dog respiratory tract, In:
Inhaled Particles IV (W. H. Walton, ed.), pt. 1, pp.
237-245, Pergamon Press, Oxford, England.
Swift, D. J., Shanty, F., and O'Neill, J. T. 1977b.
Human respiratory tract deposition of nuclei parti-
cles and health implications, Presented at American
Nuclear Society Winter Meeting, San Francisco
(November-December 1977).
Task Group on Lung Dynamics. 1966. Deposition
297
and retention models for internal dosimetry of the
human respiratory tract, Health Phys. 12:173-207.
Taulbee, D. B., and Yu, C. P. 1975. A theory of
aerosol deposition in the human respiratory tract, J.
Appl. Physiol. 38:77-85.
Thomas, R. L., and Raabe, O. G. 1978. Regional
deposition of ~37Cs-labelled monodisperse and
polydisperse aluminosilicate aerosols in Syrian
hamsters, Am. Ind. Hyg. Assoc.J. 39:100~1018.
Thomson, M. L., and Pavia, D. 1974. Particle pene-
tration and clearance in the human lung, Arch.
Environ. Health 29:21~219.
Thomson, M. L., and Short, M. D. 1969. Mucocil-
iary function in health, chronic obstructive airway
disease and asbestosis, J. Appl. Physiol. 26:535-539.
Torjussen, W., and Anderson, I. 1979. Nickel con-
centrations in nasal mucosa, plasma and urine in
active and retired nickel workers, Ann. Clin. Lab.
Sci. 9:280298.
Tryka, A. F., Sweeney, T. D., Brain, J. D., and
Godleski, J. J. 1985. Short-term regional clearance
of an inhaled submicrometric aerosol in pulmonary
fibrosis, Am. Rev. Respir. Dis. 132:606011.
Tu, K. W., and Knutson, E. O. 1984. Total deposi-
tion of ultrafine hydrophobic and hygroscopic aero-
sols in the human respiratory system, Aerosol Sci.
Technol. 3:453065.
Tyler, W. S. 1983. Comparative subgross anatomy of
lungs, Am. Rev. Respir. Dis. 128(Suppl.):S32-S36.
Valberg, P. A. 1985. Determination of retained lung
dose, In: Toxicology of Inhaled Materials (H. P.
Witschi andJ. D. Brain, eds.), pp. 57-91, Springer-
Verlag, Heidelberg.
Valberg, P. A., Brain, J. D., Sneddon, S. L., and
LeMott, S. R. 1982. Breathing patterns influence
aerosol deposition sites in excised dog lung,J. Appl.
Physiol. 53:82~837.
Valberg, P. A., Wolff, R. K., and Mauderly, J. L.
1985. Redistribution of retained particles. Effect of
hyperpnea, Am. Rev. Respir. Dis. 131:27~280.
van Antweiler, H. 1958. Uber die Function des Flim-
merepithels der Luftwege, insbesondere under
Staubbelastung, Beitr. Silikose-Forsch. 3:509.
Vastag, E., Matthys, H., Zsamboki, G., Kohler, D.,
and Daikeler, G. 1986. Mucociliary clearance in
smokers, Eur.J. Respir. Dis. 68:107-113.
Vincent, J. H., and Armbruster, L. 1981. On the
quantitative definition of the inhalability of airborne
dust, Ann. Occup. Hyg. 24:245-248.
Vostal, J. J., Chan, T. L., Garg, B. D., Lee, P. L., and
Strom, K. S. 1979. Lymphatic transport of inhaled
diesel particles in the lungs of rats and guinea pigs
exposed to diluted diesel exhaust, In: Proceedings of
the International Symposium on Health EfJects of Diesel
Engine Emission, U. S. Environmental Protection
Agency, Cincinnati, Ohio (December 1979).
Waite, D. A., and Ramsden, D. 1971. The inhalation
of insoluble iron oxide particles in the sub-micron
range, pt. I, chromium 51 labelled aerosols,
AEEW-R740, Atomic Energy Authority, United
Kingdom.
Wanner, A. 1977. Clinical aspects of mucociliary
transport, Am. Rev. Respir. Dis. 116:7~125.
Waters, M. D., Gardner, D. E., Aranyi, C., and
OCR for page 298
298
Biological Disposition of Airborne Particles
Coffin, D. L. 1975. Metal toxicity for rabbit alve-
olar macrophages in vitro, Environ. Res. 9:32-47.
Watson, A. Y., and Brain, J. D. 1979. Uptake of iron
oxide aerosols by mouse airway epithelium, Lab.
Invest. 40:450-459.
Weibel, E. R. 1963. Morphometry of the Human Lung,
Academic Press, New York.
Weibel, E. R. 1980. Design and structure of the
human lung, In: Pulmonary Diseases and Disorders
(A. P. Fishman, ed.), pp. 224-271, McGraw-Hill,
New York.
Weller, M. A., Chen, S., and Barnhart, M. I. 1980.
Acid Phosphatase in Alveolar Macrophages Ex-
posed in viva to Diesel Engine Exhaust, GM Con-
tract Publ. CR80-5/BI, General Motors Corp., De-
troit, Mich.
West, J. B., and Hugh-Jones, P. 1959. Patterns of gas
flow in the upper bronchial tree, J. Appl. Physiol.
14:75~759.
White, H. J., and Garg, B. D. 1981. Early pulmonary
response of the rat lung to inhalation of high
concentration of diesel particles, J. Appl. Toxicol.
1:104-110.
Williams, S. J., Holden, K. M., Sabransky, M., and
Menzel, D. B. 1980. The distributional kinetics of
Ni2+ in the rat lung, Toxicol. Appl. Pharmacol.
55:8~93.
Wilson, F. T., Jr., Hiller, F. C., Wilson, J. G., and
Bone, R. C. 1985. Quantitative deposition of ul-
trafine stable particles in the human respiratory
tract, J. Appl. Physiol. 58:22~229.
Wolff, R. K. 1986. Effects of airborne pollutants on
mucociliary clearance, Environ. Health Perspect. 66:
222-237.
Wolff, R. K., Dolovich, M. B., Obminski, G., and
Newhouse, M. T. 1977. Effects of exercise and
eucapnic hyperventilation on bronchial clearance in
man,J. Appl. Physiol. 43:46-50.
Wolff, R. K., Kanapilly, G. M., DeNee, P. B., and
McClellan, R. O. 1981. Deposition of 0.1 ,um chain
aggregate aerosols in beagle dogs, J. Aerosol Sci.
12:119-129.
Wolff, R. K., Kanapilly, G. M., Chang, Y. S., and
McClellan, R. O. 1982. Deposition of 0.1 ,um
aggregate and spherical 67Ga203 particles inhaled by
beagle dogs, In: Annual Report of the Inhalation
Toxicology Research Institute 1981-1982 (M. B.
Snipes, T. C. Marshall, and B. S. Martinez, eds.),
Lovelace Biomedical and Environmental Research
Institute, Albuquerque, N.Mex., National Techni-
cal Information Service, Springfield, Va.
Wolff, R. K., Henderson, R. F., Snipes, M. B.,
Griff~th, W. C., Mauderly, J. L., Cuddihy, R. G.,
and McClellan, R. O. 1987. Alterations in particle
accumulation and clearance in lungs of rats chroni-
cally exposed to diesel exhaust, Fundam. Appl.
Toxicol. 9:15~166.
Wolfsdorf, J., Swift, D. L., and Avery, M. E. 1969.
Mist therapy reconsidered: an evaluation of the
respiratory deposition of labelled water aerosols
produced by jet and ultrasonic nebulizers, Pediatrics
43:799-808.
Xu, G. B., and Yu, C. P. 1985. Deposition of inhaled
diesel emission particulates in different human age
groups at various respiratory conditions, Presented
at Annual Meeting of the American Association for
Aerosol Research, Albuquerque, N. Mex. (No-
vember 1985).
Yeates, D. B., and Aspin, M. 1978. A mathematical
description of the airways of the human lungs,
Respir. Physiol. 32:91-104.
Yeates, D. B., Aspin, M., Levison, H., Jones, M. T.,
and Bryan, A. C. 1975. Mucociliary tracheal trans-
port rates in man, J. Appl. Physiol. 39:487-495.
Yeates, D. B., Gerrity, T. R., and Garrard, C. S.
1981a. Particle deposition and clearance in the bron-
chial tree, Ann. Biomed. Eng. 9:577-592.
Yeatesj D. B., Pitt, B. R., Spektor, D. M., Karron,
G. A., and Albert, R. E. 1981b. Coordination of
mucociliary transport in human trachea and intra-
pulmonary airways, J. Appl. Physiol . 51:1057-1064.
Yeh, H. C. (ed.) 1980. Respiratory Tract Deposition
Models Final Report, DOE Research and Devel-
opment Report, LF-72, National Technical Infor-
mation Service, U.S. Department of Commerce,
Springfield, Va.
Yeh, H., and Schum, G. M. 1980. Models of human
lung airways and their application to inhaled parti-
cle deposition, Bull. Math. Biol. 42:461-480.
Yeh, H. C., Barr, E. B., and Esparza, D. C. 1980.
Deposition of inhaled dual aerodynamically similar
aerosols in Syrian hamsters, In: Respiratory Tract
Deposition Models: Final Report to NIEHS (H. C.
Yeh, ed. ), Inhalation Toxicology Research Insti-
tute, Lovelace Biomedical and Environmental Re-
search Institute, Albuquerque, N.Mex., National
Technical Information Service, Springfield, Va.
Yu, C. P., and Diu, C. K. 1982. A comparative study
of aerosol deposition in different lung models, Am.
Ind. Hyg. Assoc. J. 43:54~5.
Yu, C. P., Diu, C. K., and Soong, T. T. 1981.
Statistical analysis of aerosol deposition in nose and
mouth, Am. Ind. Hyg. Assoc. J. 42:72~733.
Yu, C. P., Hu, J. P., Leikauf, G., Spektor, D., and
Lippmann, M. 1983. Mucociliary transport and
particle clearance in the human tracheobronchial
tree, In: Aerosols in the Mining and Industrial Work
Environments (V. A. Marple and B. Y. H. Liu, eds.),
pp. 177-184, Ann Arbor Science Publishers, Ann
Arbor, Mich.
Ziegler, E. E., Edwards, B. B., Jensen, R. L., Ma-
haffey, K. R., and Fomon, S. J. 1978. Absorption
and retention of lead by infants, Pediatr. Res.
12:29-34.
Representative terms from entire chapter:
pulmonary region