Vol. 91, Issue 5, 2024-2034, November 2001
NO2 interfacial transfer is reduced by
phospholipid monolayers
Lydia M.
Connor1,
Akhil
Bidani1,
Jon
Goerke2,3,
John A.
Clements2,4, and
Edward M.
Postlethwait1
1 Pulmonary and Critical Care Medicine, Department of
Internal Medicine, University of Texas Medical Branch, Galveston,
Texas 77555; and 2 Cardiovascular Research Institute,
Departments of 3 Physiology and 4 Pediatrics, University
of California at San Francisco, San Francisco, California 94143
 |
ABSTRACT |
Nitrogen dioxide (NO2) is a ubiquitous,
pollutant gas that produces a broad range of pathological and
physiological effects on the lung. Absorption of inhaled
NO2 is coupled to near-interfacial reactions between the
solute gas and constituents of the airway and alveolar epithelial
lining fluid. Although alveolar surfactant imparts limited
resistance to respiratory gas exchange compared with that contributed
by either the pulmonary membrane or uptake in red blood cells,
resistance to NO2 flux could have a significant effect on
NO2 absorption kinetics. To investigate the effect of interfacial surfactant on NO2 absorption, we designed an
apparatus permitting exposure of variably compressed monolayers. Our
results suggest that compressed monolayers enriched in
1,2-dipalmitoyl-sn-3-glycero-phosphocholine present
significant resistance to NO2 absorption even at surface tensions greater than those achieved in vivo. However, monolayers composed of pure unsaturated phospholipids failed to alter
NO2 absorption significantly when compressed, in spite of
similar reductions in surface tension. The results demonstrate that
phospholipid monolayers appreciably limit NO2 absorption
and further that monolayer-induced resistance to NO2 flux
is related to physicochemical properties of the film itself rather than
alterations within the aqueous and gas phases. On the basis of these
findings, we propose that pulmonary surfactant may influence the
intrapulmonary gas phase distribution of inhaled NO2.
nitrogen dioxide; reactive absorption; pulmonary surfactant; interfacial resistance; lung epithelial lining fluid; dipalmitoyl
phosphatidylcholine
 |
INTRODUCTION |
NITROGEN DIOXIDE
(NO2) is a free radical atmospheric toxicant that initiates
a broad range of pulmonary pathophysiological responses. Inhalation of
NO2 induces dose-dependent effects on both conducting
airway and alveolar epithelia. Acute low-level exposures result in
oxidative stress, the induction of characteristic epithelial lesions
spanning the bronchoalveolar region, and inflammation (13,
44). Chronic NO2 exposure produces alterations in
lung architecture and obstructive lesions that result in a reduction of
both available alveolar surface area and lung compliance (13, 44). Although the pathological consequences of both acute and chronic NO2 intoxication have been extensively documented,
the mechanisms that govern NO2 intrapulmonary dispersion
and the induction of tissue injury have not been fully characterized.
The distribution of acute epithelial injury is related, in part, to the
intrapulmonary airspace concentration of NO2 and its local
rate of absorption. The pulmonary epithelium is overlain by a
continuous but inhomogeneous aqueous layer, epithelial lining fluid
(ELF), which covers all airspace surfaces and protrusions (2). Absorption of inhaled NO2 is governed by
near-interfacial reactions with ELF constituents that serve to maintain
the net driving force for the flux of NO2 from the gas
phase into the ELF, a process termed "reactive absorption"
(33). Because absorption is directly coupled to reaction,
diffusion of NO2 through the ELF is presumed to be limited
(3, 35, 52). Products formed as a consequence of reactive
absorption likely initiate the cascade of events leading to cell injury.
The small-molecular-weight antioxidants glutathione, ascorbic acid, and
uric acid have been identified as primary substrates for
NO2 reactive absorption (35, 52).
Interestingly, although unsaturated fatty acids as components of
phospholipids appear in abundance in the lung aqueous surface
compartment, under environmentally relevant conditions, NO2
reacts less with unsaturated fatty acids than with other available
substrates (14, 35, 37, 38). NO2 reactive
absorption proceeds most rapidly during electron transfer reactions
with antioxidant anions, which can exist in significant concentration
at lung ELF pH (33, 35, 52). Under quasi-steady-state,
well-mixed exposure conditions (NO2 inflow constant),
NO2 absorption rapidly attains an aqueous substrate concentration-dependent rate that does not increase with time although
the uptake efficiency is <100% (33). This phenomenon can
be observed under transient exposure conditions (NO2 as the limiting reagent) in which the first-order rate constant for the disappearance of NO2 from the gas phase plateaus despite
further increases in aqueous- phase substrate concentration or mixing (34). These in vitro studies are in agreement with
theoretical analyses that suggest that appreciable mass transfer
limitations are present at the gas-liquid interface (3,
10).
Pulmonary surfactant functions to prevent alveolar collapse at
end-expiratory lung volumes by lowering surface tension and, thereby,
maintaining high lung compliance (9, 47). The most abundant surface active component is
1,2-dipalmitoyl-sn-3-glycero-phosphocholine (DPPC), which
may be enriched within the monomolecular film present at the air-liquid
interface (30, 51). In general, the flux of respiratory
gases across the serial resistances encountered in transit from the air
space to red blood cells (e.g., surface fluid compartment, tissue,
plasma, and red blood cell) is thought to proceed with limited
restriction (53). However, previous experimental evidence
suggests that the physicochemical characteristics of the gas-liquid
interface may influence the flux of molecules between the gas and
aqueous phases. For example, interfacial films of oils and aliphatic
alcohols have been demonstrated to limit significantly the in vitro
rate of water evaporation (1, 23), CO2
absorption (4), and O2 transport
(21) across gas-liquid interfaces and to restrict the rate
of gas-liquid reactions (10). On the basis of these
previous observations, we investigated whether monolayers of surface
active phospholipids alter the interfacial flux (absorption) of
NO2. We utilized an in vitro exposure apparatus, which
facilitated 1) control of phospholipid monolayer and aqueous phase composition, 2) continuous measurement of surface
tension, and 3) determination of steady-state
NO2 absorption rates.
 |
METHODS |
Reagents.
DPPC, 1-palmitoyl-2-oleoyl-sn-glycero-3-phosphocholine
(POPC),
1,2-dipalmitoyl-sn-glycero-3-phospho-rac-glycerol
(DPPG),
1-palmitoyl-2-oleoyl-sn-glycero-3-phospho-rac-glycerol (POPG), and 1,2-dilinoleoyl-sn-glycero-3-phosphocholine
(DLPC), all in powder form, were purchased from Avanti Polar Lipids
(Alabaster, AL) and used as received. Glutathione (GSH), ascorbic acid
(AH2), desferrioxamine, and SeKem agarose were purchased
from Sigma Chemical (St. Louis, MO). Tween 80, HPLC-grade chloroform,
methanol, and isopropanol and all other reagents, of analytical grade,
were purchased from Fisher Scientific (Houston, TX). NO2
and nitric oxide cylinders were purchased from Liquid Carbonic
(Pasadena, TX) as certified standards in N2.
Surfactant isolation.
Surfactant was isolated from viral antigen-free, 250-275 g, male
Sprague-Dawley rats (Harlan Sprague Dawley, Houston, TX). The protocol
for harvesting bronchoalveolar lavage fluid (BALF) was approved by the
Animal Care Use Committee of the University of Texas Medical Branch,
Galveston. Animals were allowed free access to water and food before
induction of anesthesia. Animals were anesthetized with 70 mg/kg
intraperitoneal pentobarbital sodium and, after tracheal cannulation
and midline thoracotomy, lungs were lavaged in situ five times with 9.0 ml of 0.15 M NaCl. The BALF was pooled, centrifuged at 150 × g for 10 min to remove cells and debris and
subsequently at 60,000 × g for 2.5 h to isolate the surface-active components (modified from Stevens et al., Ref. 50). The pellet was extracted by a modified Bligh-Dyer
method (5), with subsequent double reextraction of the
upper aqueous phase. The pooled crude extract was dried under
N2 and redissolved in chloroform for gravimetric estimation
of total extractable material. These weights probably overestimate the
true phospholipid weights because of the presence of other lipids and
hydrophobic proteins. For surface deposition, solutions (1 mg/ml) were
prepared in chloroform, stored under N2 at
20°C, and
used within 72 h.
Compressed monolayer studies.
An exposure probe-surface balance with a pantographic barrier was
utilized to examine NO2 absorption across phospholipid
monolayers at several surface tensions (24 ± 1°C) (Fig.
1A). Surface tension was
measured as described below. The glass probe was modeled after a
previously described design (48). Briefly, pollutant gas
entered the probe chamber via a sidearm port and exited around a disk such that flow proceeded centrally over a defined surface area (28.3 cm2) (Fig. 1B). The sampling line of the
nitrogen oxides (NOx) analyzer (see below) was
connected to the exit port to actively withdraw gas through the central
tube. Gas flow into the exposure system exceeded the sampling rate by
10-15%. The compression apparatus consisted of a stainless steel,
Teflon ribbon-lined pantograph frame (17 × 25 cm) mounted in a
Plexiglas dish (20 × 45 cm), which contained the aqueous phase.
Phospholipids were deposited within the pantograph frame from
chloroform solutions (1 mg/ml) by use of a 25-µl syringe to achieve
an initial area per molecule of 121 Å2/molecule (~0.1
µg/cm2). The compression system was mounted on a moveable
platform to permit adjustment of the distance between the aqueous
surface and the bottom edge of the probe. The entire apparatus was
isolated in an enclosure to prevent room air currents from disturbing
the flow pattern under the probe.

View larger version (21K):
[in this window]
[in a new window]
|
Fig. 1.
Schematic representation of the exposure
probe-surface balance apparatus. Individual components are
identified by letters. A: Pantograph barrier. Glass exposure
probe (a); hinged, deformable stainless steel frame with Teflon ribbon
lining (maximum surface area = 387 cm2, minimum
surface area = 157 cm2) (b); platinum plate (c); and
manual leadscrew (d). Plexiglas dish (in which the compression frame
was mounted), adjustable platform, force transducer assembly and
enclosure are not shown. B: Vertical cross-section of the
probe and aqueous interface: gas inlet port (e); has exit port to
nitrogen oxides (NOx) analyzer (f), central restriction
disk (g), height = 5 mm (h), and clearance = 1 mm (i).
|
|
NO2 exposure protocols.
For exposure of compressed films, 500 ml of buffer (10 mM potassium
phosphate, pH 7.0) with or without GSH (1.0 mM) was placed in the
Plexiglas dish, and the aqueous surface was cleaned by aspiration. The
system was raised to achieve a 1-mm separation between the bottom
surface of the probe and the aqueous surface. The probe gas inlet and
exit lines were connected, and the system enclosure was closed. After a
10-min control exposure period, a phospholipid monolayer was deposited
from solvent through a port and allowed to equilibrate for 5 min.
Subsequently, three full compression-expansion cycles were performed
before compression to the final set area(s) to achieve a uniform
phosphatidylcholine (PC) film devoid of bare areas.
Alternatively, exposures were conducted in a different apparatus
utilizing 50-ml flat-bottom Erlenmeyer flasks (33) when it
became necessary either to limit the aqueous phase volume or to prevent
contamination of the compression system. For these exposures, 10 ml of
buffer (10 mM or 50 mM potassium phosphate, pH 7.0) with or without GSH
(1.0-50.0 mM) or AH2 (1.0 mM) was introduced into the
flask. A phospholipid film was deposited at a nominal surface density
of 0.5 µg/cm2 onto a surface area of 15.9 cm2
and allowed to equilibrate for 10 min before NO2 delivery.
Flasks were equipped with a Teflon-lined stopper with inlet and exit ports that extended within 1.0 and 5.0 cm above the interface, respectively, with the outlet port being sampled by the NOx
analyzer. Films were not compressed after spreading in this system.
Exposures generally lasted 30-45 min. Inlet NO2
concentrations ([NO2]i) were determined
before and after each exposure with the probe or flask out of line.
NO2 exposures.
Exposures conducted in both the probe and flask systems were performed
under unstirred, quasi-steady-state conditions (NO2 inflow
constant) at 25°C unless stated otherwise (34). For most studies, [NO2]i was <10 ppm. In this range,
NO2 absorption displays first-order kinetics with respect
to [NO2]i (34). GSH (1.0 mM) was
used most often as the aqueous substrate because it effectively drives
NO2 absorption (35, 52) and can be maintained
in stable concentration with limited autoxidation. Exposure atmospheres were generated by countercurrent injection of high-concentration NO2 (in N2) into temperature-equilibrated,
humidified air by using mass flow controllers (Scott Specialty Gas,
Houston, TX) adjusted to achieve the appropriate final NO2
concentrations. Inlet gas flow was controlled to exceed sample flow by
10-15% (128.9 ± 2.4 or 150.9 ± 7.2 ml/min) for both
the probe and flask systems. NO2 exit concentrations were
continuously monitored using a model 42 chemiluminescence NO
NO2 NOx analyzer (Thermoenvironmental, Franklin, MA). The analyzer internal pump sampled at a rate of 112.9 ± 1.6 or 131.8 ± 2.25 ml/min (flow increased after
scheduled pump maintenance) irrespective of the exposure apparatus
used. The analyzer was routinely calibrated by using a primary standard of 10 ppm NO. Occasionally, analysis of gas phase NO2 was
performed via the Saltzman procedure (17) in which a known
volume of exit gas was directly withdrawn into a 50-ml glass syringe
containing 10 ml Saltzman reagent (33), and the
concentration was determined on the basis of daily standard curves. In
both types of apparatus, NO2 absorption was computed on the
basis of the mass balance across the exposure system and expressed as
either 1) the absorption rate per unit surface area
{([NO2]i
[NO2]e) · outlet flow/surface area}, where [NO2]e is NO2
concentration at the exit port, or 2) the fractional
uptake {([NO2]i
[NO2]e)/[NO2]i}.
Theoretical analyses of the probe exposure system characteristics and
the derivation of a film resistance term considered in the
DISCUSSION are contained in the APPENDIX.
Surface tension measurements.
Surface tension (
) was measured by using a flamed 2.5-cm-wide
roughened platinum plate. Before phospholipid deposition, the aqueous
surface was thoroughly cleaned by aspiration such that
= 71 ± 3 mN/m (25°C) was maintained during several
compression-expansion cycles. Surface tension was measured directly on
all monolayers studied in the probe-surface balance apparatus. Because
of geometric limitations, surface tension measurements for the flask
studies were determined separately on films contained in open glass
vessels of equivalent interfacial geometry.
Reaction product analyses.
Both probe and flask aqueous pools were sampled for reaction products.
Nitrite (NO
) concentrations were determined via the
Greiss reaction (36) using standards containing 1.0 mM
GSH. Glutathione analyses were performed via HPLC (18).
Briefly, immediately after the termination of an exposure, 1.5 ml of
aqueous phase was withdrawn, diluted 1:2 in HPLC mobile phase, and
stored at 4°C in the dark. Samples (15 µl) were injected onto a
15 × 150-mm Waters C18 Novapak column and eluted isocratically at
1.0 ml/min by using 3% methanol in 10 mM phosphate buffer (pH 3.0)
containing 50 µM tetrabutyl-ammonium hydrogen sulfate. Peaks were
detected at 220 nm and integrated to compute peak area. GSH was
estimated on the basis of standard curve peak areas. Each sample was
analyzed in triplicate, and a mean peak area was used to compute concentration.
Data analysis.
All values are expressed as means ± SD. Mean differences between
groups were tested by ANOVA and Dunnett's test post hoc
(49). Significance was defined as P < 0.05.
 |
RESULTS |
Effect of DPPC monolayers on NO2 absorption.
DPPC monolayers were deposited onto 1.0 mM GSH solutions and exposed to
NO2 for up to 1 h. During the course of a single
exposure, after the three initial compression-expansion cycles,
monolayers were compressed to four set areas from an initial molecular
area of 121 to 49 Å2/molecule. The presence of the probe
prevented further reductions in interfacial surface area or surface
tension. Between 10 and 15 min were allotted at each stage of
compression to permit determination of NO2 absorption as
well as measurement of stable surface tensions. As demonstrated in Fig.
2, when the DPPC monolayers were
cyclically compressed and reexpanded, NO2 absorption rates
were coupled to surface tension. NO2 uptake decreased
linearly with surface tension (Fig. 3;
r = 0.99), attaining a maximal reduction of 47% from the monolayer-free surface value (P < 0.05). On
compression, NO2 uptake rates were stable over > 45-min periods.

View larger version (13K):
[in this window]
[in a new window]
|
Fig. 2.
Effect of cyclic surface compression on simultaneously
recorded surface tension (A) and NO2
concentration ([NO2]) at exit port
([NO2]e) (B).
1,2-Dipalmitoyl-sn-3-glycero-phosphocholine (DPPC)
monolayers were deposited onto 1.0 mM glutathione (GSH) and exposed to
5.2 ppm NO2. Monolayers were compressed in the surface
balance reducing surface area by 60% at maximum compression (from an
initial phospholipid surface density of 121 Å2/molecule)
through 3 compression and 2 expansion cycles. Plots represent typical
compression/expansion cycles that preceded monolayer exposures at
selected set area(s). Decreasing the area in the absence of a surface
film did not change either surface tension or [NO2] in
the exit gas. The plot of [NO2] slightly lags the plot of
monolayer surface tension because of delayed NO2 analyzer
response.
|
|

View larger version (9K):
[in this window]
[in a new window]
|
Fig. 3.
Relationship between NO2 absorption and
surface tension with graded compression of DPPC monolayers in the
surface balance. DPPC was deposited at an initial surface density of
121 Å2/molecule (~0.1 µg/cm2) onto 1 mM
GSH solutions and exposed to 5.2 ppm NO2 for ~45 min at
25°C. Monolayers were compressed in stepwise fashion while
[NO2]e was monitored for ~10 min at each
compression point. Surface tensions of 71.4 ± 1.5, 60.6 ± 1.3, 53.8 ± 2.0, 47.2 ± 4.5, and 26.5 ± 4.4 were
recorded at areas of 387, 230, 203, 186, and 157 cm2,
respectively. NO2 absorption decreased linearly
(r = 0.99) with surface tension. At the end of each
experiment, [NO2]e returned to baseline
levels on surface reexpansion. Values are means ± SD for n
6.
|
|
Similar results were obtained when exposures were conducted at elevated
temperatures (~30°C, [NO2] = 7.6 ± 0.2 ppm,
44.3 ± 1.7, and 34.5 ± 2.3 ng · min
1 · cm
2 without
and with compressed DPPC, respectively, data not shown). In contrast to
previous observations (33), under the experimental conditions employed we observed only a modest rise in NO2
uptake when the temperature of uncompressed DPPC systems was increased. Background NO2 loss was approximately twofold greater at
the elevated temperature, likely because of condensation of water on
system surfaces, increased NO2 reaction with water, and
increased diffusivity of solute NO2 and nitrite within the
aqueous phase. The limited temperature effect likely resulted from an
inability to maintain the elevated temperatures (initial
temperature
37°C) so that analyses were conducted under
somewhat lower actual temperatures (gas phase
31°C, bulk
liquid temperature
29°C). However, compression consistently induced significant decreases in the NO2
absorption rates.
Surface tension dependence.
Because NO2 uptake fell with surface tension, we
investigated whether this was related to surface tension or the nature
of the interfacial film. To do this, we used a soluble detergent, Tween
80, to reduce surface tension, and we conducted NO2
exposures using GSH + Tween 80 mixtures. To avoid possible
contamination of the compression system by the Tween 80, we used the
exposure flasks. A 0.1% solution of Tween 80 satisfied the criteria of significantly reducing basal surface tensions (70.3 ± 3.6 to
39.5 ± 2.2 mN/m, P < 0.05) while also permitting
the deposition of stable phospholipid films. Despite reductions in
surface tension, Tween 80 solutions failed to reduce the rate of
GSH-mediated NO2 absorption (Fig.
4). By comparison, when DPPC monolayers
(Fig. 3) were compressed to the same average surface tension achieved by 0.1% Tween 80 alone (
= 39.5 ± 2.2 mN/m), DPPC
monolayers reduced NO2 absorption ~32%. Similarly, when
DPPC films were deposited (0.5 µg/cm2) onto Tween 80 solutions, NO2 uptake significantly declined by 52% (Fig.
4), suggesting that the presence of saturated interfacial phospholipids, rather than surface tension per se, inhibited
NO2 flux.

View larger version (20K):
[in this window]
[in a new window]
|
Fig. 4.
Effect of detergent on NO2 absorption. Buffer
or 0.1% Tween 80 solutions with or without 1 mM GSH were exposed to
4.6 ppm NO2 for 15 min in the presence (hatched bar) or
absence (open bars) of a DPPC film in the flask system. DPPC was
deposited at an initial surface density of 0.5 µg/cm2 and
allowed to equilibrate for 15 min before exposure initiation. Despite
achieving low surface tensions (listed above bars), 0.1% Tween 80 had
no effect on NO2 absorption. NO2 absorption was
significantly reduced, however, when DPPC monolayers were deposited
onto the Tween 80 solutions. Although surface tension was further
reduced by the DPPC (24.3 mN/m), it did not differ from surface
tensions achieved with buffer + DPPC in the absence of Tween 80 (25 mN/m). *NO2 uptake was significantly lower when DPPC
was added to the Tween-GSH-containing system (ANOVA; P < 0.05). Values are means ± SD for n 5.
|
|
Gas-phase NO2 and aqueous-phase substrate concentration
dependence.
The gas-phase concentration dependence of monolayer-induced effects was
investigated utilizing the probe/surface balance apparatus with
[NO2]i between 4 and 125 ppm. The Saltzman
procedure for NO2 analysis was employed for
[NO2]i > 20 ppm. DPPC monolayers were
deposited onto GSH solutions and exposed to 4, 9, 19, or 125 ppm
NO2 for 30 min. DPPC-induced reductions in NO2
uptake were significant (P < 0.05) at all
NO2 concentrations studied (Fig.
5).

View larger version (21K):
[in this window]
[in a new window]
|
Fig. 5.
Relationship between NO2 gas phase
concentration at inlet port ([NO2]i) and
monolayer-induced effects on NO2 absorption (A)
and fractional uptake (B). DPPC monolayers, deposited at an
initial surface density of 121 Å2/molecule onto 1 mM GSH
in the surface balance, were exposed to 4, 10, 20, 90, or 125 ppm
NO2 (DPPC uncompressed = open bars, DPPC
compressed = hatched bars). Exposures of uncompressed monolayers
proceeded for 10 min followed by maximal compression (achieving a 60%
reduction in surface area) and continued exposure for an additional 20 min. At [NO2] > 20 ppm, monolayers were allowed to
equilibrate in the absence of NO2 gas flow, and gas phase
analysis was performed by using Saltzman reagent (17).
Values are means ± SD for n 3. *Uptakes are
significantly lower for compressed DPPC systems compared with matched
uncompressed systems (ANOVA; P < 0.05).
|
|
Exposures were also conducted to determine whether substrate
composition and concentration influenced the observed monolayer-induced effect on NO2 absorption. Flask exposures were conducted
with DPPC films deposited onto solutions containing 1.0 mM
AH2 and exposed to 5 ppm NO2 for 30 min.
Desferrioxamine (50 µM) was added to AH2 solutions to
limit autoxidation. As in the experiments with GSH,
AH2-mediated NO2 absorption was significantly
reduced from 48.0 ± 0.4 to 16.6 ± 1.2 ng · min
1 · cm
2, suggesting
that the monolayer-induced effects were independent of aqueous
substrate composition. In a separate series of experiments, the effect
of interfacial films was assessed over a broad range of substrate GSH
concentrations. Again DPPC films were deposited onto solutions
containing 1, 10, or 50 mM GSH. Relative to the GSH controls, the
addition of DPPC films significantly decreased NO2
absorption regardless of substrate concentration (Fig.
6).

View larger version (12K):
[in this window]
[in a new window]
|
Fig. 6.
Aqueous substrate concentration dependence of
monolayer-induced reduction in NO2 absorption. In flask
exposures, excess DPPC was deposited at a nominal surface density of
0.5 µg/cm2 onto solutions containing 1, 10, and 50 mM GSH
concentration ([GSH]). Exposures were conducted at 6.1 ± 0.1 ppm
NO2 for 15 min at 25°C under unstirred, steady-state
exposure conditions. Values are means ± SD for n
5.
|
|
Reaction product analysis.
To investigate whether monolayer-induced decrements in NO2
absorption were related to altered reaction pathways, we measured GSH
utilization and the reaction products of NO2. Under
physiological conditions, NO2 undergoes quantitative
univalent reduction to NO
. Both probe and flask
exposures were conducted to determine whether surface films modulated
the stoichiometry between NO2 uptake and
NO
formation (Table
1). For the probe exposures, a round
Teflon dish (66 × 4 mm internal dimensions) was submerged in the
aqueous phase directly beneath the probe to help restrict reaction
product diffusion and subsequent dilution into the trough bulk phase. Samples were pipetted from the dish. The results were similar to
previous analyses (31, 52) in that we observed an
approximate 1:1 ratio of NO
formation to
NO2 uptake regardless of the exposure system or the
presence of a compressed monolayer. For the GSH utilization studies,
flask systems and lower GSH concentrations (200 µM) were used. DPPC
films were deposited onto buffer or GSH solutions and exposed for 45 min. HPLC analyses revealed that the profile and proportions of
reaction products, relative to NO2 uptake, were unaltered
by the presence of a DPPC film (data not shown). In the presence of a
DPPC film, NO2 absorption and GSH consumption were
significantly reduced. NO2 uptake (421 ± 25 or
232 ± 15 nmol without or with PC, respectively) was less than GSH
consumption (709 ± 45 or 514 ± 37 nmol without or with PC,
respectively) because of secondary redox cycling reactions (52). Together, the data suggest that the decline in
NO2 uptake was not related to alterations in the reaction
kinetics between NO2 and the aqueous-phase substrates.
Effect of monolayer composition on NO2 absorption.
Although it is generally accepted that pulmonary surfactant present at
the interface is enriched in DPPC (8, 19), whether unsaturated fatty acyl moieties are retained throughout
compression-expansion cycles remains equivocal (24, 39).
We investigated the effects of interfacial unsaturated fatty acids on
NO2 uptake utilizing monolayers composed of either DLPC or
POPC. Although not a component of natural surfactant, DLPC was of
particular interest both as a potential direct reaction substrate for
NO2 (because of the abundant unsaturated bonds) and because
of molecular packing properties induced by the two unsaturated fatty
acyl moieties. On compression, despite surface tension reductions,
monolayers of DLPC and POPC did not significantly decrease
NO2 absorption rates (Fig.
7).

View larger version (28K):
[in this window]
[in a new window]
|
Fig. 7.
Lack of effect of unsaturated PC on NO2
absorption. Phospholipids were deposited at an initial surface density
of 121 Å2/molecule onto 1 mM GSH in the surface
balance and exposed to 4.8 ppm NO2. Bars are coded as in
Fig. 4 with double-hatched bars representing unsaturated
phosphatidylcholine (PC) films. Exposures of uncompressed films
proceeded for 10 min followed by maximal compression (achieving a 60%
reduction in surface area) with continued exposure for an additional 20 min. Neither
1-palmitoyl-2-oleoyl-sn-glycero-3-phosphocholine (POPC) nor
1,2-dilinoleoyl-sn-glycero-3-phosphocholine (DLPC) reduced
NO2 absorption on compression, although surface tensions
(listed above bars) achieved were similar to those with DPPC. Values
are means ± SD for n 4. *NO2 uptake for
the DPPC-covered system was significantly less than that of the
uncompressed control (ANOVA; P < 0.05).
|
|
Alveolar surfactant is a complex mixture containing both saturated and
unsaturated lipids. Consequently, studies utilizing BALF extracts and
phospholipid mixtures were also conducted to examine monolayer systems
more representative of natural surfactant. Rat BALF lipid extract,
although a crude preparation, was used as a surrogate of natural
surfactant, and DPPC-POPG (9:1; wt/wt) and DPPC-POPC-DPPG (70:27:3;
wt/wt/wt) mixtures were prepared to simulate published compositions of
human surfactant phospholipids and fatty acids (41).
Phospholipid stock solutions (1 mg/ml in chloroform) were prepared by
using an averaged molecular weight based on the percent composition of
each phospholipid in the solution. All three compressed monolayers
significantly reduced NO2 absorption (Fig.
8). The reductions varied with the
concentration of unsaturated moieties, resulting in a barrier
effectiveness hierarchy of DPPC > DPPC-POPG > DPPC-POPC-DPPG. Despite failing to lower surface tension below 44 mN/m,
the BALF extract impeded NO2 uptake significantly.

View larger version (27K):
[in this window]
[in a new window]
|
Fig. 8.
Effect of interfacial phospholipid composition on
NO2 absorption in the surface balance. Mixed monolayer
systems in which the relative concentration of DPPC varied were exposed
to NO2 (4.6 ± 0.2 ppm) as described in Fig. 7. Stock
solutions of the phospholipid mixtures (1 mg/ml in chloroform) were
prepared on the basis of either a weighted average or estimated
molecular weights for pure chemical and bronchoalveolar lavage fluid
(BALF) systems, respectively. DPPG,
1,2-dipalmitoyl-sn-glycero-3-phospho-rac-glycerol;
POPG,
1-palmitoyl-2-oleoyl-sn-glycero-3-phospho-rac-glycerol.
Double-hatched bars indicate uptakes in the presence of films.
*NO2 absorption was decreased significantly in all cases
(ANOVA; P < 0.05). Surface tensions achieved on
compression (listed above bars) were similar among the pure chemical
systems. Although surface tension remained high for BALF extract,
NO2 uptake was significantly decreased. Values are
means ± SD for n 3.
|
|
 |
DISCUSSION |
Investigations into the influences of surface films on gas-vapor
transport processes began in the mid-1920s. Initial studies were
directed at evaluating the effect of monomolecular oil films on the
rate of water evaporation (23, 27, 40). In the early 1940s, Langmuir and Schaefer (23) designed and utilized an
apparatus for evaluating monolayer effects on the rate of water
evaporation. These studies, along with those that followed, suggested
that interfacial monolayers of some fatty acids and aliphatic alcohols significantly reduced the rate of water evaporation (1,
42). However, several years passed before the concept of lung
surfactant film permeability was first introduced: it was initially
discussed in the context of a mathematical model (7)
evaluating the stability of bubbles expressed from lung by Pattle
(29). Although studies assessing interfacial lung
surfactant permeability to water vapor have been conducted
(25), monolayer effects on the rate of gas flux from the
gas to the aqueous phase have received limited attention (e.g., 4, 21).
This may be due in large part to the fact that O2 and
CO2 partial pressures normally equilibrate rapidly between alveolar gas and pulmonary capillary blood (43).
Characterizing the influences of interfacial phospholipids on
NO2 absorption required an exposure model that would enable measurement of changes in NO2 gas phase concentration over
a defined surface during controlled compression of the surface film. We were limited to an in vitro approach because interfacial conditions within the lung cannot be tightly controlled. Although studies were
conducted under quasi-steady-state exposure conditions, intrapulmonary NO2 concentrations vary throughout ventilation. However,
previous studies have demonstrated that processes governing
NO2 absorption were equivalent under quasi-steady-state and
transient (NO2-limiting) exposure conditions (32,
34). Despite the design limitations of the compression-exposure
apparatus that prevented compression of surface films to very low
tensions (Fig. 1), the system permitted reproducible control and study
of the effects of interfacial, gas-phase, and aqueous-phase conditions
on NO2 absorption.
Using the probe exposure apparatus, we observed that compression of
DPPC monolayers to surface tensions still substantially above those
reached in vivo (e.g., 25 vs. <1 mN/m) significantly reduced the rate
of NO2 absorption (Figs. 3, 6, 7). Increases in monolayer
packing, indicated by lower surface tensions, were rapidly followed by
reduced NO2 absorption (Fig. 2). We therefore felt it
important to evaluate whether the decreased uptake was due to
additional resistance imposed directly at the interface or to changes
in the gas- and/or aqueous-phase conditions. NO2 diffuses
through the gas-phase boundary layer, dissolves in the aqueous-phase
boundary layer, and reacts within a near-interfacial zone. Because of
the limited aqueous solubility of NO2, saturation of the
aqueous boundary layer should occur rapidly in the absence of reactive
substrates (3). The driving force for the continued net
flux of NO2 is maintained by diffusion of both
NO2 and reactive substrates (e.g., GSH, AH2)
into the reaction zone. Chemical reaction of NO2 serves to
limit both its diffusion into the bulk aqueous phase and the
development of backpressures resulting from accumulation of dissolved
NO2. Previous kinetic studies, demonstrating that NO2 gas-phase disappearance rates were independent of
aqueous bulk-phase volume and equivalent for both wetted filter
material and aqueous bulk-phase systems, support these concepts
(34). Studies employing 1% agarose to gel the aqueous
phase demonstrated that impeding aqueous-phase convection did not alter
the steady-state rates of NO2 uptake compared with
unstirred controls (data not shown). In the probe exposure studies,
stable uptake rates were observed over prolonged periods with or
without either compressed monolayers or reaction substrates. It is
unlikely that monolayer compression caused a backpressure-induced
decrease in NO2 flux due to aqueous substrate limitations
because this would imply that solute diffusion would be constrained to
a new, lower steady-state level.
Although previous NO2 studies have shown limitations to
mass transfer in the gas phase (3), we concluded that the
addition of a monolayer would not affect gas-phase NO2
transport. Nevertheless, appreciable mass transfer resistance is
associated with the gas phase as is shown by the saturation of
NO2 absorption rates in the presence of vigorous
interfacial stirring and aqueous substrates in great excess (e.g.,
[NO2]
10 ppm, GSH concentration
10 mM)
(33, 34). NO2 absorption in the presence of an
uncompressed DPPC film did reach maximal values (Fig. 6) similar to
those reported previously under steady-state, well-stirred conditions
(33). We attributed the reduction in NO2
absorption observed with DPPC to resistance introduced by the
interfacial films themselves rather than effects of the films on the
adjacent bulk phases. We based this conclusion on the following
considerations: 1) the constant background loss of
NO2 in buffer systems despite the absence or presence of
DPPC, 2) the theoretical lack of monolayer-induced diffusion
effects within the aqueous reaction zone, 3) the lack of
direct surface tension effects on absorption (Fig. 4), 4) a film-induced reduction in NO2 absorption at various aqueous
substrate concentrations and compositions, and NO2
gas-phase concentrations (Fig. 5), and 5) the consistent
stoichiometry of NO
formation from NO2
(Table 1). It is noteworthy that DPPC films reduced NO2
uptake significantly even at 90 and 125 ppm (~60%, Fig. 5). These
data clearly demonstrate that interfacial monolayers limit
NO2 transfer.
Despite their lowering of surface tension to ~25 mN/m, unsaturated PC
moieties did not restrict NO2 transfer (Fig. 7). The area
per molecule of unsaturated PC in a fully compressed monolayer remains
quite high (e.g., POPC > 70 Å2/molecule)
(11) compared with disaturated PC (<49
Å2/molecule). Moreover, had exposure-induced oxidation of
the unsaturated fatty acid occurred, the products would have further
disordered molecular packing. NO2 reaction with unsaturated
fatty acids proceeds via either allylic hydrogen abstraction or
double-bond addition (15, 16). For polyunsaturated fatty
acids, the molecule isomerizes and adds O2 to produce a
cis-trans conjugated diene fatty acid hydroperoxide. For both mono- and polyunsaturates, NO2
addition products may potentially result (22, 38). The
conformational changes induced by these molecular modifications could
have introduced further disorder into the films (20).
Others have reported monolayer-induced resistance to transport
processes ranging from <1 to 103 s/cm (4, 23,
48). Estimates of film resistance, which we calculated from the
data of Sebba and Briscoe (48) (for C16-C20 fatty
acid and aliphatic alcohols), ranged from <0.1 to 25 s/cm, with the
exception of n-docosanol, which achieved a resistance of 180 s/cm when maximally compressed. Blank and Roughton (4) reported resistance to CO2 transport across (C16-C18
fatty acid and aliphatic alcohol) films of 80-392 s/cm. Clements
(7) estimated the film resistance of Pattle's bubbles
(surfactant bubbles extruded from whole lung) to be ~104
s/cm (180 s/cm when the solubility coefficient of air in water is taken
into account). A plot of film resistance vs. surface pressure (Fig.
9) clearly demonstrates that film
resistance is related to the degree of DPPC monolayer compression.
Under the exposure conditions employed in these studies, monolayer
resistance to NO2 absorption increased from 0.3 to 12.3 s/cm when the film was compressed from 121 to 49 Å2/molecule. Because the surface tensions achieved in
these studies were still higher than those that occur in vivo, and film
molecular packing was lower, it is reasonable to speculate that
physiological resistance to NO2 transfer within the
pulmonary gas exchange regions could exceed those observed in this
study. Differences in estimates of film resistance between previous
studies and those reported herein likely reflect variations in
experimental materials and methods and in the definition of film
resistance.

View larger version (10K):
[in this window]
[in a new window]
|
Fig. 9.
Relationship between interfacial resistance to
NO2 flux and DPPC surface pressure. As discussed in the
APPENDIX, film resistance is defined as the difference
between total resistance and apparatus resistance.
|
|
We cannot be sure that NO2 absorption would have continued
to decrease during surface compression to lower, physiological levels
of surface tension; however, the relation is reasonably linear in the
range of surface tension measured (Fig. 3). Nevertheless, it is likely
that the low resistance of mixed monolayers would be raised by further
compression, which produces a more DPPC-enriched film. Furthermore,
alveolar surface tension varies throughout the ventilation cycle even
during tidal breathing: large increases in lung volume increase
alveolar surface tension above equilibrium (25 mN/m) (46),
at which point renewal of the surfactant monolayer begins. Interfacial
lipids are probably also responsible for the low surface tension of
conducting airway lining fluid (30 mN/m) (45). As
demonstrated by the Tween 80 (Fig. 4) and unsaturated fatty acid (Fig.
7) studies, mere reduction in surface tension is not sufficient to
restrict NO2 transfer. Consequently, because airway
interfacial properties have not been fully characterized, it is
difficult to predict whether significant film resistance to
NO2 transfer might occur in these anatomic sites.
The implications of these results are intriguing. If NO2
absorption in proximal air spaces is limited by interfacial surfactant, then NO2 movement into more distal regions would occur. In
contrast, the absence of exposure-induced injury has been accepted as
prima facie evidence for the lack of NO2 distribution into
distal alveoli. The intrapulmonary distribution of inhaled reactive
gases is related to the balance between removal at the airway walls and
longitudinal transport (3, 6). Dosimetry models predict
that the gas-phase concentration of inhaled NO2 rapidly
declines beyond the proximal alveolar spaces (26, 28).
Most models, which attempt to characterize the tissue dose of inhaled
oxidants, predict a rapid equilibration between gas and aqueous (ELF)
phases on the basis of Henry's law solubility coefficients
(3). Data from our studies lead us to speculate that the
resistance of surfactant films to NO2 diffusion could
result in increased NO2 transport to more distal airspaces. If uptake were sufficiently restricted, cell injury would not directly
correlate with the local gas-phase [NO2] concentration. Furthermore, because in vitro exposure models (e.g., cell cultures) generally do not include an interfacial film of surfactant, dose-effect relationships may differ appreciably from those occurring in vivo. Consequently, differing relationships between gas-phase concentration and cell injury may confound direct extrapolations between in vitro
exposure models and from models to animals.
 |
APPENDIX |
Validation of probe exposure apparatus.
Because of the design characteristics of the probe apparatus, some
NO2 loss to the atmosphere was inevitable (Fig. 1). To evaluate NO2 flow characteristics under the probe and to
determine optimal probe positioning, round filters wetted with Saltzman reagent (17) were placed on a solid support and positioned
directly beneath the probe, and the pattern of color development was
examined. When 1) the central restriction disc was recessed
4 mm from the probe lip and 2) the probe lip was positioned
1 mm above the wetted filter, a circular pattern of homogeneous
staining (34.1 ± 1 cm2) formed on the wetted filters.
The surface area of the colored circle was similar to that of the probe
itself (28.3 cm2) and was not altered when exposures were
conducted with the pantograph barrier set to the smallest allowable
surface area.
The background (buffer without GSH) rate of NO2 gas phase
disappearance {([NO2]i
[NO2]e) · exit flow · surface
area
1} represents the combined contributions of aqueous
solubility and reaction with water (which is relatively slow; Ref.
12). The background rates among buffer only, buffer plus
DPPC (121 Å2/molecule), and buffer plus compressed DPPC
(49 Å2/molecule) systems were comparable (data not shown),
indicating that monolayer-induced effects on transfer were small under
these conditions. In addition, the rates of NO2 gas-phase
disappearance were comparable for GSH solutions with or without
uncompressed DPPC or POPC (121 Å2/molecule) (23.0 ± 0.4, 23.1 ± 0.3, and 23.1 ± 0.4 ng · min
1 · cm
2 for GSH,
DPPC, and POPC, respectively). Collectively, the data suggest that the
gas phase distribution under the probe was not appreciably affected by
the presence of a monolayer.
When GSH solutions were exposed to NO2 under the probe, the
exit concentration remained constant for >45 min, indicating
steady-state uptake over the time intervals used in our experiments and
suggesting that the thickness of the NO2 reaction zone
remained constant, allowing a calculation of the NO2
gradient across the monolayer.
Derivation of film resistance.
We derived a mathematical expression for film resistance under the
probe on the basis of the following assumptions: 1) a steady state existed during the measurements of uptake, 2) the
profile of changing stagnant layer thickness in the gas phase was not affected by the surface films, 3) an edge-to-center
NO2 gradient existed, 4) vertical gradients in
gas-phase [NO2] were negligible, 5) the
effective depth of the reaction zone was constant, and 6)
specific film resistance was equal to the difference between total
resistance (probe-flask system with PC deposited onto GSH solution,
Rtotal) and probe resistance (probe-flask system with GSH
solution alone, Rapparatus).
We used a washer-shaped control volume, of thickness h with
inner radius r and outer radius r +
r, to perform a steady-state mole balance on
NO2 (Eq. 1).
|
(1)
|
where
is the outlet gas flow (ml/min), C is
[NO2] in the gas phase (mol/ml), and N is
NO2 flux from gas to liquid
(mol · cm
2 · min
1). By
assuming that
is constant, Eq. 1 can be rearranged
to
|
(2)
|
Taking the limit as
r
0, this equation becomes
|
(3)
|
We then defined the rate equation for interfacial flux as
|
(4)
|
where R is the interfacial resistance (s/cm),
Cliquid is [NO2] at the aqueous surface, and
is the solubility of NO2 in the aqueous phase. Assuming
that the backpressure from the liquid is negligible (N
C/R) and
|
(5)
|
integrating Eq. 5 yields
|
(6)
|
where subscripts i and f refer to initial and final parameters,
(i.e., radii or concentration) so that
|
(7)
|
We then defined specific film resistance as the difference
between Rtotal, the system resistance (GSH with PC
deposited) and Rapparatus, probe resistance (GSH alone). R,
therefore, represents a composite coefficient that includes the effects
of surface adsorption, aqueous solubility, diffusion, and chemical
reaction of NO2.
 |
ACKNOWLEDGEMENTS |
Assistance in the design and construction of specialized equipment
by Frederick Schuster and Gordon Ansell and technical assistance of
Leon Katigbak are gratefully acknowledged. We are also indebted to a
referee for an alternative derivation of the equation for film resistance.
 |
FOOTNOTES |
This work was supported in part by National Heart, Lung, and Blood
Institute Grants HL-54696 and HL-24075 and by National Institute of
Environmental Health Sciences Grants 5-F31-ES05749 and T32-ES-07254 (to
L. M. Connor).
Address for reprint requests and other correspondence: E. M. Postlethwait, Environmental Toxicology, Dept. of Preventive Medicine & Community Health, Univ. of Texas Medical Branch, 301 Univ. Blvd., Galveston, TX 77555-1110 (E-mail: epostlet{at}utmb.edu).
The costs of publication of this
article were defrayed in part by the
payment of page charges. The article
must therefore be hereby marked
"advertisement"
in accordance with 18 U.S.C. Section 1734 solely to indicate this fact.
Received 27 March 2001; accepted in final form 9 July 2001.
 |
REFERENCES |
1.
Archer, RJ,
and
La Mer VK.
The rate of evaporation of water through fatty acid monolayers.
J Physic Chem
59:
200-208,
1955.
2.
Bastacky, J,
Lee CYC,
Goerke J,
Koushafar H,
Yager D,
Kenaga L,
Speed TP,
Chen Y,
and
Clements JA.
Alveolar lining layer is thin and continuous: low-temperature scanning electron microscopy of rat lung.
J Appl Physiol
79:
1615-1628,
1995[Abstract/Free Full Text].
3.
Bidani, A,
and
Postlethwait EM.
Complexities in Structure and Function of the Lung. New York: Dekker, 1998, p. 243-296.
4.
Blank, M,
and
Roughton FJW
The permeability of monolayers to carbon dioxide.
Trans Faraday Soc
56:
1832-1841,
1960.
5.
Bligh, EG,
and
Dyer WJ.
A rapid method of total lipid extraction and purification.
Can J Biochem Physiol
37:
911-917,
1959.
6.
Bush, ML,
Raybold T,
Abeles S,
Hu SC,
Ben-Jebria A,
and
Ultman JS.
Longitudinal distribution of ozone absorption in the lung: simulation with a single path model.
Toxicol Appl Pharmacol
140:
219-226,
1996[ISI][Medline].
7.
Clements, JA.
Surface tension of lung extracts.
Proc Soc Exp Biol Med
95:
170-172,
1957.
8.
Clements, JA.
Pulmonary surfactant.
Am Rev Respir Dis
101:
984-990,
1970[ISI][Medline].
9.
Clements, JA,
Hustead RF,
Johnson RP,
and
Gribetz I.
Pulmonary surface tension and alveolar stability.
J Appl Physiol
16:
444-450,
1961[Abstract/Free Full Text].
10.
Dankwerts, PV.
Gas-Liquid Reactions. New York: McGraw-Hill, 1970, p. 66-69.
11.
Demel, RA,
van Kessel WSMG,
and
van Deenen LLM
The properties of polyunsaturated lecithins in monolayers and liposomes and the interactions of these lecithins with cholesterol.
Biochim Biophys Acta
266:
26-40,
1972[Medline].
12.
England, C,
and
Corcoran WH.
Kinetics and mechanisms of the gas-phase reaction of water vapor and nitrogen dioxide.
Ind Eng Chem Fundam
13:
373-384,
1974.
13.
Evans, MJ.
Oxidant gases.
Environ Health Perspect
55:
85-95,
1984[ISI][Medline].
14.
Finlayson-Pitts, BJ,
Sweetman LL,
and
Weissbart B.
A Fourier transform infrared spectrometry study of the reactions of phosphatidylcholines with gaseous N2O5 and NO2.
Toxicol Appl Pharmacol
89:
438-448,
1987[ISI][Medline].
15.
Giamalva, DH,
Kenion GB,
Church DF,
and
Pryor WA.
Rates and mechanisms of reaction of nitrogen dioxide with alkenes in solution.
J Am Chem Soc
109:
7059-7063,
1987.
16.
Huie, RE.
The reaction kinetics of NO2.
Toxicology
89:
193-216,
1994[ISI][Medline].
17.
Intersociety Committee for Air Sampling and Analysis.
Methods for air sampling and analysis. Washington, DC: American Public Health Association, 1977, p. 524-534.
18.
Jayatilleke, E,
and
Shaw S.
A high-performance liquid chromatographic assay for reduced and oxidized glutathione in biological samples.
Anal Biochem
214:
452-457,
1993[ISI][Medline].
19.
Keough, KMW
Membrane Fluidity in Biology. New York: Academic, 1985, p. 39-84.
20.
Keough, KMW,
and
Kariel N.
Differential scanning calorimetric studies of aqueous dispersions of phosphatidylcholines containing two polyenoic chains.
Biochim Biophys Acta
902:
11-18,
1987[Medline].
21.
Ladanyi, E,
Ahuja RC,
Mobius D,
and
Stalder K.
Oxygen Transport to Tissue. New York: Plenum, 1992, vol. XIV, p. 343-348.
22.
Lai, CC,
and
Finlayson-Pitts BJ.
Reactions of dinitrogen pentoxide and nitrogen dioxide with 1-palmitoyl-2-oleoyl-sn-glycero-3-phosphocholine.
Lipids
26:
306-314,
1991[ISI][Medline].
23.
Langmuir, I,
and
Schaefer VJ.
Rates of evaporation of water through compressed monolayers on water.
J Franklin Inst
235:
119-162,
1943.
24.
Lipp, MM,
Lee KYC,
Waring A,
and
Zasadzinski JA.
Fluorescence, polarized fluorescence, and Brewster angle microscopy of palmitic acid and lung surfactant protein B monolayers.
Biophys J
72:
2783-2804,
1997[Abstract/Free Full Text].
25.
Meban, C.
Evaporative resistance of pulmonary surfactant films.
Experientia
37:
867-868,
1981[ISI][Medline].
26.
Miller, FJ,
Overton JH,
Myers ET,
and
Graham JA.
Air Pollution by Nitrogen Oxides. Amsterdam: Elsevier, 1982, p. 377-387.
27.
Notter, RH,
and
Berg JC.
Transport resistance of dipalmitoyl and rat lung lecithin films.
J Colloid Interface Sci
45:
421-424,
1973.
28.
Overton, JH,
and
Graham RC.
Simulation of the uptake of a reactive gas in a rat respiratory tract model with an asymmetric tracheobronchial region patterned on complete conducting airway cast data.
Comput Biomed Res
28:
171-190,
1995[ISI][Medline].
29.
Pattle, RE.
Properties, function and origin of the alveolar lining layer.
Nature
175:
1125-1127,
1955[Medline].
30.
Perez-Gil, J,
Tucker J,
Simatos G,
and
Keough KMW
Interfacial adsorption of simple lipid mixtures combined with hydrophobic surfactant protein from pig lung.
Biochem Cell Biol
70:
332-338,
1992[ISI][Medline].
31.
Postlethwait, EM,
and
Bidani A.
Pulmonary disposition of inhaled NO2-nitrogen in isolated rat lungs.
Toxicol Appl Pharmacol
98:
302-312,
1989.
32.
Postlethwait, EM,
and
Bidani A.
Mechanisms of pulmonary NO2 absorption.
Toxicology
89:
217-237,
1994[ISI][Medline].
33.
Postlethwait, EM,
Langford SD,
and
Bidani A.
Reactive absorption of nitrogen dioxide by pulmonary epithelial lining fluid.
J Appl Physiol
69:
523-531,
1990[Abstract/Free Full Text].
34.
Postlethwait, EM,
Langford SD,
and
Bidani A.
Interfacial transfer kinetics of NO2 into pulmonary epithelial lining fluid.
J Appl Physiol
71:
1502-1510,
1991[Abstract/Free Full Text].
35.
Postlethwait, EM,
Langford SD,
Jacobson LM,
and
Bidani A.
NO2 reactive absorption substrates in rat pulmonary surface lining fluids.
Free Radic Biol Med
19:
553-563,
1995[ISI][Medline].
36.
Postlethwait, EM,
and
Mustafa MG.
Fate of inhaled nitrogen dioxide in isolated perfused rat lung.
J Toxicol Environ Health
7:
861-872,
1981[ISI][Medline].
37.
Prutz, WA,
Monig H,
Butler J,
and
Land EJ.
Reactions of nitrogen dioxide in aqueous model systems: oxidation of tyrosine units in peptides and proteins.
Arch Biochem Biophys
243:
125-134,
1985[ISI][Medline].
38.
Pryor, WA,
Lightsey JW,
and
Church DF.
Reaction of nitrogen dioxide with alkenes and polyunsaturated fatty acids: addition and hydrogen abstraction mechanisms.
J Am Chem Soc
104:
6685-6692,
1982.
39.
Rana, FR,
Mautone AJ,
and
Dluhy RA.
Surfactant chemistry of binary mixtures of phospholipids in monolayers. Infrared studies of surface composition at varying surface pressures in a pulmonary surfactant model system.
Biochemistry
32:
3169-3177,
1993[Medline].
40.
Rideal, EK.
On the influence of thin surface films on the evaporation of water.
J Phys Chem
38:
1585-1588,
1924.
41.
Rooney, SA.
Treatise on Pulmonary Toxicology: Comparative Biology of the Normal Lung. Boca Raton, FL: CRC Press, 1992, p. 511-544.
42.
Rosano, HL,
and
La Mer VK.
The rate of evaporation of water through monolayers of esters, acids and alcohols.
J Phys Chem
60:
348-353,
1956.
43.
Roughton, FJW,
and
Forster RE.
Relative importance of diffusion and chemical reaction rates in determining rate of exchange of gases in the human lung, with special reference to true diffusing capacity of pulmonary membrane and volume of blood in the lung capillaries.
J Appl Physiol
11:
290-302,
1957[Abstract/Free Full Text].
44.
Schlesinger, RB.
Environmental Toxicants. New York: Van Nostrand Reinhold, 1992, p. 412-451.
45.
Schürch, S,
Gehr P,
Hof VI,
Geiser M,
and
Green F.
Surfactant displaces particles toward the epithelium in airways and alveoli.
Respir Physiol
80:
17-32,
1990[ISI][Medline].
46.
Schürch, S,
Goerke J,
and
Clements JA.
Direct determination of surface tension in the lung.
Proc Natl Acad Sci USA
73:
4698-4702,
1976[Abstract/Free Full Text].
47.
Schürch, S,
Green FHY,
and
Bachofen H.
Formation and structure of surface films: captive bubble surfactometry.
Biochim Biophys Acta
1408:
180-202,
1998[Medline].
48.
Sebba, F,
and
Briscoe VA.
The evaporation of water through unimolecular films.
J Chem Soc (Lond)
1:
106-118,
1940.
49.
Sokal, RR,
and
Rohlf FJ.
Biometry. New York: Freeman, 1981.
50.
Stevens, PA,
Wright JR,
and
Clements JA.
Changes in quantity, composition and surface activity of alveolar surfactant at birth.
J Appl Physiol
63:
1049-1057,
1987[Abstract/Free Full Text].
51.
Van Liempd, JPJG,
Boonman AAH,
Demel RA,
Gieles PMC,
and
Gorree TCM
Nonselective squeeze-out of dioleoylphosphatidylcholine and dioleoylphosphatidylglycerol from binary mixed monolayers with dipalmitoylphosphatidylcholine.
Biochim Biophys Acta
897:
495-501,
1987[Medline].
52.
Velsor, LW,
and
Postlethwait EM.
NO2-induced generation of extracellular reactive oxygen is mediated by epithelial lining layer antioxidants.
Am J Physiol Lung Cell Mol Physiol
273:
L1265-L1275,
1997[Abstract/Free Full Text].
53.
Weibel, ER.
Morphological basis of alveolar-capillary gas exchange.
Ph