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Fluticasone Propionate Protects against Ozone-Induced Airway Inflammation and Modified Immune Cell Activation Markers in Healthy Volunteers

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Ozone exposure induces airway neutrophilia and modifies innate immune monocytic cell-surface phenotypes in healthy individuals. High-dose inhaled corticosteroids can reduce O(3)-induced airway inflammation, but their effect on innate immune activation is unknown. We used a human O(3) inhalation challenge model to examine the effectiveness of clinically relevant doses of inhaled corticosteroids on airway inflammation and markers of innate immune activation in healthy volunteers. Seventeen O(3)-responsive subjects [>10% increase in the percentage of polymorphonuclear leukocytes (PMNs) in sputum, PMNs per milligram vs. baseline sputum] received placebo, or either a single therapeutic dose (0.5 mg) or a high dose (2 mg) of inhaled fluticasone proprionate (FP) 1 hr before a 3-hr O(3) challenge (0.25 ppm) on three separate occasions at least 2 weeks apart. Lung function, exhaled nitric oxide, sputum, and systemic biomarkers were assessed 1-5 hr after the O(3) challenge. To determine the effect of FP on cellular function, we assessed sputum cells from seven subjects by flow cytometry for cell-surface marker activation. FP had no effect on O(3)-induced lung function decline. Compared with placebo, 0.5 mg and 2 mg FP reduced O(3)-induced sputum neutrophilia by 18% and 35%, respectively. A similar effect was observed on the airway-specific serum biomarker Clara cell protein 16 (CCP16). Furthermore, FP pretreatment significantly reduced O(3)-induced modification of CD11b, mCD14, CD64, CD16, HLA-DR, and CD86 on sputum monocytes in a dose-dependent manner. This study confirmed and extended data demonstrating the protective effect of FP against O(3)-induced airway inflammation and immune cell activation.
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Environmental Health Perspectives
VOLUME 116 | NUMBER 6 | June 2008
799
Research
|
Environmental Medicine
Ozone is a commonly encountered environ-
mental air pollutant. In epidemiologic investi-
gations, exposure to increased levels of
ambient air O
3
has been associated with exac-
erbations of asthma, chronic obstructive pul-
monary disease (COPD), and pneumonia,
generally 24–48 hr after exposure occurs
(Bernstein et al. 2004; Peden 2001).
Controlled chamber exposures to O
3
cause an
influx of neutrophils to the airway and a
decrease in lung function, although these two
effects do not correlate with each other, indi-
cating that separate mechanisms account for
these effects (Bernstein et al. 2004). O
3
expo-
sure also causes increased responsiveness to
allergen in allergic asthmatics (Peden 2001).
We have recently observed that O
3
exposure
can also result in increased expression of
CD11b, CD14, CD16, CD80, CD86, and
HLA-DR on airway dendritic cells (DCs),
monocytes, and macrophages (Alexis et al.
2004b). It has been suggested that the action
of O
3
on airway neutrophils, monocytes, and
macrophages accounts for much of the disease
outcomes associated with O
3
exposure. These
inflammatory events also mimic the type of
inflammation that occurs with acute viral and
bacterial infection and exacerbations of
asthma and COPD (Maneechotesuwan et al.
2007; Pauwels 2004).
Together, these observations suggest that
O
3
challenge may be a useful controlled
human disease model for screening novel anti-
inflammatory pharmaceutical agents in phase I
proof-of-concept trials. Holz et al. (2005)
tested the utility of a 0.25-ppm O
3
challenge
as a drug efficacy screen, using a single pre-
treatment dose of the established anti-
inflammatory agents fluticasone propionate
(FP) and oral prednisolone as test agents in a
randomized three-arm crossover study in
18 healthy subjects comparing the effect of
these two treatments with that of placebo on
O
3
-induced airway inflammation. Holz et al.
(2005) reported that, compared with placebo,
pretreatment with 2 mg inhaled FP and 50 mg
oral prednisolone resulted in a significant
reduction in post-O
3
sputum neutrophils per
milliliter (by 62% and 64%, respectively) and
myeloperoxidase (MPO; by 55% and 42%,
respectively). These results demonstrated that
corticosteroids do inhibit the proinflammatory
actions of O
3
.
In the present study, we sought to extend
these observations by comparing the effect of
a single administration of a high dose of
inhaled FP (2 mg) with a dose that is
employed in clinical practice for asthma and
COPD (0.5 mg) and placebo. Given the
importance that monocytes, macrophages,
and DCs likely have in the pathophysiology of
O
3
-induced exacerbations of disease, we also
examined the effect of these treatments on
expression of CD11b/CR3, mCD14,
CD16/FcγRIII, CD64/FcγRI, CD86/B7, and
HLA-DR on monocytes, macrophages, and
DCs recovered from airway sputum. Clara cell
protein 16 (CCP16) and surfactant protein D
(SP-D) are innate immune molecules and
products of airway epithelial cells (Haczku
2006) that can be released to the circulation
during lung injury (Holz et al. 2005). CCP16
is induced in the serum of subjects exposed to
O
3
challenge (Blomberg et al. 2003). We have
previously shown that SP-D levels in the lung
are significantly altered after O
3
inhalation in
mice (Kierstein et al. 2006), but whether simi-
lar changes can be detected in the human
serum is not known. Thus, we evaluated
CCP16 and SP-D for their potential utility as
serum biomarkers for assessing the effects of
inhaled corticosteroids on O
3
injury in the
respiratory tract.
Materials and Methods
Subjects. Seventeen (nine male and eight
female) nonsmoking healthy volunteers
(10 from the Center for Environmental
Medicine, Asthma and Lung Biology; 7 from
Rancho Los Amigos National Rehabilitation
Center) between 18 and 50 years of age (age,
26.4 ± 7.4 years, mean ± SD; body mass
index, 20–30 kg/m
2
) were recruited for this
Address correspondence to N.E. Alexis, Center for
Environmental Medicine, Asthma and Lung
Biology, University of North Carolina, 104 Mason
Farm Rd., Chapel Hill, NC 27599-7310 USA.
Telephone: (919) 966-9915. Fax: (919) 966-9863.
E-mail: Neil_Alexis@med.unc.edu.
We thank M. Almond, M. Herbst, H. Wells,
F. Dimeo, and L. Newlin-Clapp for their technical
assistance with this study.
This work was supported by GlaxoSmithKline and
by the National Institutes of Health (grant ES012706).
R.T.-S. is employed by GlaxoSmithKline, the
manufacturer of fluticasone proprionate. The
remaining authors declare they have no competing
financial interests.
Received 15 October 2007; accepted 27 February
2008.
Fluticasone Propionate Protects against Ozone-Induced Airway Inflammation
and Modified Immune Cell Activation Markers in Healthy Volunteers
Neil E. Alexis,
1,2
John C. Lay,
1
Angela Haczku,
3
Henry Gong,
4,5
William Linn,
4,5
Milan J. Hazucha,
1
Brad Harris,
1
Ruth Tal-Singer,
6
and David B. Peden
1,2
1
Center for Environmental Medicine, Asthma and Lung Biology, and
2
Department of Medicine, University of North Carolina, Chapel Hill,
North Carolina, USA;
3
Department of Medicine, University of Pennsylvania, Philadelphia, Pennsylvania, USA;
4
Department of Medicine,
University of California, Los Angeles, California, USA;
5
Environmental Health Service, Rancho Los Amigos National Rehabilitation
Center, Downey, California, USA;
6
GlaxoSmithKline, King of Prussia, Pennsylvania, USA
BACKGROUND: Ozone exposure induces airway neutrophilia and modifies innate immune monocytic
cell-surface phenotypes in healthy individuals. High-dose inhaled corticosteroids can reduce
O
3
-induced airway inflammation, but their effect on innate immune activation is unknown.
O
BJECTIVES: We used a human O
3
inhalation challenge model to examine the effectiveness of clini-
cally relevant doses of inhaled corticosteroids on airway inflammation and markers of innate
immune activation in healthy volunteers.
M
ETHODS: Seventeen O
3
-responsive subjects [> 10% increase in the percentage of polymorpho-
nuclear leukocytes (PMNs) in sputum, PMNs per milligram vs. baseline sputum] received placebo,
or either a single therapeutic dose (0.5 mg) or a high dose (2 mg) of inhaled fluticasone proprionate
(FP) 1 hr before a 3-hr O
3
challenge (0.25 ppm) on three separate occasions at least 2 weeks apart.
Lung function, exhaled nitric oxide, sputum, and systemic biomarkers were assessed 1–5 hr after
the O
3
challenge. To determine the effect of FP on cellular function, we assessed sputum cells from
seven subjects by flow cytometry for cell-surface marker activation.
R
ESULTS: FP had no effect on O
3
-induced lung function decline. Compared with placebo, 0.5 mg
and 2 mg FP reduced O
3
-induced sputum neutrophilia by 18% and 35%, respectively. A similar
effect was observed on the airway-specific serum biomarker Clara cell protein 16 (CCP16).
Furthermore, FP pretreatment significantly reduced O
3
-induced modification of CD11b, mCD14,
CD64, CD16, HLA-DR, and CD86 on sputum monocytes in a dose-dependent manner.
C
ONCLUSIONS: This study confirmed and extended data demonstrating the protective effect of FP
against O
3
-induced airway inflammation and immune cell activation.
K
EY WORDS: inhaled corticosteroids, innate immune markers, ozone, sputum neutrophils Environ
Health Perspect 116:799–805 (2008). doi:10.1289/ehp.10981 available via http://dx.doi.org/ [Online
28 February 2008]
study. All subjects underwent a thorough
physical examination and had no history of
cardiovascular or chronic respiratory disease
and were free of upper or lower respiratory
tract infection at least 4 weeks before study
participation. All subjects had a forced expira-
tory volume in 1 sec (FEV
1
) of at least 80%
predicted for a normal population of similar
weight and height. A positive urine pregnancy
test resulted in exclusion of female subjects
from the study. The use of prescription drugs,
over-the-counter medication (e.g., aspirin and
nonsteroidal anti-inflammatory drugs), vita-
mins, antioxidants, and dietary supplements
was not permitted for the duration of the
study. All study participants were able to pro-
duce an adequate sputum sample ( 1 × 10
6
total cells, 50% cell viability, 20% squa-
mous epithelial cells) as measured on their first
baseline visit (sputum with no O
3
exposure),
and all were responsive to O
3
(defined as
10% increase in total and percent sputum
neutrophils) (Holz et al. 2005) after exposure
to 0.25 ppm O
3
for 3 hr with intermittent
moderate exercise (ventilation
expiratory
=
12.5 L/min/m
2
body surface area) as measured
on the second study visit. The study was
approved by the Committee on the Protection
of the Rights of Human Subjects, School of
Medicine, University of North Carolina at
Chapel Hill, and by the Institutional Review
Board at the Rancho Los Amigos National
Rehabilitation Center. Informed written con-
sent was obtained from all subjects before their
participation in the study.
Study design. This was a double-blind,
placebo-controlled, single-dose, randomized,
three-period crossover study conducted at two
sites. Controlled O
3
exposures were performed
in comparable chamber setups at both the
University of North Carolina, Chapel Hill and
the Rancho Los Amigos facility (Alexis et al.
2004a; Gong et al. 1998). All subjects under-
went 3-hr exposures to 0.25 ppm O
3
with
intermittent moderate exercise (15 min rest,
15 min exercise at 12.5 L/min/m
2
body surface
area) at screening visit 2 and each study session
thereafter (visits 3–5). Based on FP half-life and
washout of sputum neutrophils after O
3
expo-
sure (Holz et al. 2005), O
3
exposures were sep-
arated by a minimum of 2 weeks to avoid
carryover effects. FEV
1
and forced vital capacity
(FVC) were also measured for the purpose of
assessing subject safety. Sputum induction was
performed at screening visits and at 3 hr after
the conclusion of each O
3
exposure (i.e., post-
exposure). Sputum was analyzed for total and
differential leukocyte count and fluid-phase
components and in a subset of subjects (n =7)
for cell-surface phenotypes and cell function by
flow cytometry. The study design, including
measurement time points, is depicted in
Figure 1. FP was provided as a metered dry
powder inhaler (Diskus; GlaxoSmithKline,
Research Triangle Park, NC). Each Diskus
device contained 60 × 0.5 mg doses of FP. A
matching placebo Diskus was also provided.
Subjects were randomized to receive one of
the following treatment regimens: a) 0.5 mg
FP (one inhalation of 0.5 mg FP plus three
inhalations of placebo); b) 2 mg FP (one
inhalation of 0.5 mg FP plus three inhalations
of 0.5 mg FP); and c) placebo (one inhalation
of placebo plus three inhalations of placebo).
The study staff observed each subject using
the Diskus during clinic visits to ensure that
the device was used correctly.
Pulmonary function. We used both
spirometry and impulse oscillometry (IOS) to
assess lung function status in subjects.
Spirometry was assessed at preexposure,
immediately postexposure, and then at 1-hr
intervals for 3 hr. IOS was assessed at pre-
exposure, and then hourly for 3 hr beginning
1 hr postexposure. Airway resistance and air-
way reactance were determined by IOS (Jaeger
MS-IOS and LAB Manager Software, version
4.53.2; Jaeger, Hoechberg, Germany) using
the recommended techniques of the manufac-
turer and as previously described (Singh et al.
2006). Real-time recordings of mouth pres-
sure and flow signals pulsed through 5- to
35-Hz spectrum were superimposed on trac-
ings of tidal breathing and displayed on a
computer screen. Measurements of total respi-
ratory resistance, resonant frequency (F
res
),
reactance at 5 Hz, and low-frequency reac-
tance area (area of reactance integrated from
5 Hz up to F
res
) were recorded at the 5-, 10-,
15-, and 20-min time points after the IOS test
challenge. Spirometry was performed accord-
ing to current American Thoracic Society
spirometry standards (Enright 2003).
Sputum induction and processing and
fluid-phase analyses. Subjects provided an
induced sputum sample during the screening
visit and at 3 hr post-O
3
exposure. The sputum
induction and processing methods have been
previously described in detail (Alexis et al.
2003, 2006). In brief, three 7-min inhalation
periods of nebulized hypertonic saline (3%,
4%, 5%; Devilbiss UltraNeb 99 ultrasonic neb-
ulizer; Sunrise Medical, Somerset, Somerset,
PA) were followed by expectoration of sputum
into a sterile specimen cup. Sputum cell aggre-
gates (cellular mucus plugs) were macroscopi-
cally identified and manually selected from
their surrounding fluid and treated with 0.1%
dithiothreitol (DTT; Sputolysin, Calbiochem,
San Diego, CA). Total cell counts and cell via-
bility were determined using a Neubauer
hemacytometer and trypan blue (Sigma
Chemical Co., St. Louis, MO) exclusion
staining. Differential cell counts were ana-
lyzed using the Hema-Stain-3 kit (Fisher
Diagnostics, Middletown, VA). Aliquots of
DTT-treated sputum supernatant were imme-
diately frozen and stored at –80°C for later
analysis of MPO and total protein by multi-
plex assay (Pierce Biotechnology, Rockford,
IL). All soluble factors (cytokines and
chemokines) in sputum (MPO, total protein)
were analyzed by a contract laboratory (HFL,
Fordham, UK) using validated commercial
Alexis et al.
800
VOLUME 116 | NUMBER 6 | June 2008
Environmental Health Perspectives
Figure 1. Schematic of the study design. Abbreviations: PLA, placebo; Spiro, spirometry; V, visit. The study
was a double-blinded, randomized, cross-over design with a 2-week washout period between visits. Except
for the first visit (screen) and last visit (follow-up), all visits included an O
3
exposure (0.25 ppm, 3 hr).
Baseline screen (V1)
O
3
challenge (V2)
Sputum, spiro, eNO, IOS
Spiro, eNO, IOS
3 randomized visits (V3, V4, V5)
Preexposure
PLA, 0.5 mg FP, or 2 mg FP
O
3
exposure (0.25 ppm)
Postexposure
Spiro, eNO, IOS
Spiro, eNO, IOS
Intermittent exercise
Follow-up (V6)
–3 weeks
–2 weeks
Spiro, eNO
Spiro, eNO, IOS
Spiro, eNO, IOS
Sputum, spiro, IOS, eNO
Systemic markers, CCP16, SP-D (
n
= 10), eNO
Systemic markers, CCP16, SP-D (
n
= 7)
7–10 days
–2 hr
–1 hr
0 hr
1 hr
2 hr
3 hr
+ 1 hr
+ 2 hr
+ 3 hr
+ 4 hr
+ 5 hr
eNO
enzyme-linked immunosorbent assay (ELISA)
kits. All compounds were validated in the pres-
ence of DTT. The limits of detection after
dilution (to minimize potential effects of DTT
and to achieve sufficient volume for measure-
ments) were 40 µg/mL for total protein
(Dojindo Molecular Technologies, Inc.,
Gaithersburg, MD) and 36 ng/mL for MPO
(Immundiagnostik, Bensheim, Germany).
For a subset of samples, remaining cells
were resuspended in Hank’s balanced salt
solution and kept on ice for immediate use in
flow cytometric assays for selected cell-surface
molecules and phagocytosis.
Systemic biomarkers. Venipuncture was
performed at 4 or 5 hr after O
3
exposures to
obtain serum for Multiplex systemic biomarker
analysis of tumor necrosis factor-α (TNF-α),
interferon-γ (INF-γ), interleukin-6 (IL-6),
IL-1β, IL-1Ra, IL-17, eotaxin, and IL-12P40
using fluorometric custom-designed validated
Multiplex kits (Pathway Diagnostics, Malibu,
CA). CCP16 and SP-D were assayed using
commercially available ELISA kits (Biovendor,
Candler, NC) according to the manufacturer’s
instructions.
Flow cytometry and immunofluorescent
staining. All flow cytometry acquisitions and
analyses (surface markers, phagocytosis) were
performed as previously described (Alexis
et al. 2000a) using a FACSort flow cyto-
meter (Becton Dickinson, Franklin Lakes,
NJ) and CellQuest Pro v5.3 software (Becton
Dickinson).
Cell-surface phenotypes. Immuno-
fluorescent staining and flow-cytometry
methodology have been described in detail in
previous publications (Alexis et al. 2003,
2006). In brief, cells (100 µL, 1 × 10
6
/mL)
were incubated with 10 µL fluorochrome-
labeled monoclonal antibodies, washed in
Dulbecco’s phosphate-buffered saline (DPBS),
fixed with 0.5% paraformaldehyde in DPBS,
and analyzed by flow cytometry within 48 hr
of fixation. Viable macrophages, monocytes,
neutrophils, lymphocytes, and DCs in spu-
tum were initially identified and gated on the
basis of light-scatter properties and positive
expression for CD45 (pan-leukocyte marker).
Cell populations were then confirmed by
positive staining with CD16 (neutrophils),
mCD14 (monocytes), HLA-DR (macro-
phages), HLA-DR/CD86 (DCs), and CD3
(lymphocytes). The acquired data were ana-
lyzed using CellQuest Pro v5.3 software, and
results were expressed as a rightward shift
from control in mean fluorescence intensity
(MFI) on histogram analysis. Control cells
were incubated with appropriately labeled iso-
typic control antibodies. Surface markers ana-
lyzed included markers of innate (CD11b/
CR3, mCD14/LPS receptor, CD16/FcγRIII,
CD64/FcγRI) and adaptive (HLA-DR/MHC
class II, and CD86/B7.2 co-receptor)
immune function. All monoclonal antibodies
were purchased from Beckman Coulter
Corporation (Miami, FL).
Phagocytosis. We analyzed phagocytosis
using fluorescein isothiocyanate–labeled IgG-
opsonized Saccharomyces cerevisiae zymosan-A
BioParticles (Molecular Probes, Eugene, OR)
as previously described (Alexis et al. 2003,
2006). All samples were analyzed by flow
cytometry within 24–48 hr of fixation in 1%
paraformaldehyde. Particle uptake was dis-
played on histograms and identified as a
rightward shift in MFI of the phagocytic
population versus autofluorescence of the
unlabeled control cells.
Exhaled nitric oxide. We measured
exhaled NO (eNO) levels preexposure, imme-
diately after exposure, and then at 1-hr inter-
vals for 4 hr according to standardized
procedures jointly recommended by the
American Thoracic Society and the European
Respiratory Society (2005) using a NIOX
NO analyzer (Aerocrine AB, Solna, Sweden).
Statistical analysis. To determine the total
number of neutrophils and fluid-phase mark-
ers (MPO, protein) in induced sputum 6 hr
postchallenge, we analyzed data following a
natural logarithmic transformation using a
mixed effects model, with period and treat-
ment fitted as fixed effects and subject as a
random effect. The suitability of the transfor-
mation was assessed by examining the model
residuals. Treatment effects were evaluated in
terms of treatment ratios and were calculated
as the antilog for the differences between the
least squares means; 95% confidence intervals
(CIs) were determined using pooled estimates
of variance for the least squares means differ-
ence and then antilogged.
For assessment of differences between spe-
cific treatment conditions (postscreen O
3
chal-
lenge vs. placebo vs. both doses of FP) for
CCP16, SP-D, systemic cytokines, and cell-
surface marker expression in the subset (n =7)
of volunteers studied at University of North
Carolina, Chapel Hill, we used nonparametric
one-way analysis of variance for repeated meas-
ures (Friedman test) and Dunn’s post hoc
analysis of specific pairs of variables. An overall
significance level of p < 0.05 was considered to
be significant. All values are expressed as mean
± SE. We used GraphPad Prism 3.1 software
(GraphPad Software, Inc., San Diego, CA) for
statistical analysis.
Results
Patient demographics and overall safety.
Seventeen volunteers participated in the study;
patient demographics are outlined in Table 1.
No serious adverse events were reported dur-
ing this study.
Effects of FP on 0.25 ppm O
3
-induced
changes in pulmonary function. O
3
exposure
caused decreases in FVC and FEV
1
during all
exposures. Decrements in FVC and FEV
1
were evident immediately after O
3
exposure
during placebo, 0.5 mg, and 2 mg FP treat-
ments but were subsiding by 1 hr post-
exposure for each treatment condition
(Table 2). Decrements in FVC and FEV
1
were minimal by 3 hr postexposure (Table 2).
Neither dose of FP had a statistically signifi-
cant effect on O
3
-induced lung function
changes compared with placebo. No consis-
tent O
3
-induced changes were observed in
IOS end points at any postexposure time
point (Table 2).
Effects of FP on 0.25 ppm O
3
-induced
changes in sputum neutrophils and fluid-
phase markers of neutrophil activation
(MPO, total protein). Analysis of percent
neutrophil levels post-O
3
challenge yielded
evidence of a statistically significant difference
for both active treatments (0.5 mg and 2 mg
FP) relative to placebo. Mean ± SE levels of
percent polymorphonuclear leukocytes
(PMNs) for placebo and 0.5 mg and 2 mg FP
were 54 ± 5.4%, 44 ± 4.5%, and 35 ± 3.6%,
respectively (Figure 2), which reflect an 18%
and 35% reduction in sputum percent PMNs
for 0.5 mg and 2 mg FP, respectively. The
data indicate a dose–response pattern.
FP also affected the relatively more variable
total number of neutrophils/mL. The mean
(95% CI) numbers of PMNs/mL were 66.05 ×
10
4
cells/mL (34.78–125.41 cells/mL),
56.87 × 10
4
cells/mL (30.15–107.27 cells/mL),
and 37.49 × 10
4
cells/mL (19.89–70.68
cells/mL) for placebo, 0.5 mg FP, and 2 mg
FP, respectively, 3 hr post-O
3
exposure.
These values reflected 14% fewer neutrophils
in sputum when subjects were pretreated
with 0.5 mg FP and statistically significantly
(p < 0.05) fewer neutrophils (43%) when
pretreated with 2 mg FP, indicating a dose–
response effect on the total number of
neutrophils per milliliter. In terms of vari-
ability, the neutrophil responses on the
O
3
/placebo visit versus the O
3
-only visit were
very similar for both percent neutrophils
(mean ± SE, 54 ± 5% vs. 55 ± 5%) and the
absolute number of neutrophils per mil-
ligram sputum [mean (95% CI), 66.05 × 10
4
cells/mL (34.78 to 125.41 cells/mL) vs.
Fluticasone propionate protects against airway inflammation
Environmental Health Perspectives
VOLUME 116 | NUMBER 6 | June 2008
801
Table 1. Subject demographics (
n
= 17).
Characteristic Mean ± SE
Age (years) 26.4 ± 1.8
Sex
Female 9
Male 8
Race
Caucasian 10
African American 3
American Hispanic 2
Asian 1
Other 1
Height (cm) 170 ± 2.6
Weight (kg) 78 ± 3.9
62.20 × 10
4
cells/mL (–10.17 to 312.97
cells/mL), respectively]. Other than percent
macrophages, FP exerted no statistically
significant effect on total leukocytes per milli-
liter or total and percent eosinophils, lympho-
cytes, and bronchial epithelial cells. Relative to
placebo, we observed a 24% and 48% increase
in percent macrophages with 0.5 mg and 2 mg
FP, respectively.
We observed no statistically significant
treatment effect of 0.5 mg or 2 mg FP on
MPO or total protein levels in sputum. There
was, however, borderline evidence of a differ-
ence in levels of the MPO/total protein ratio
relative to placebo for 2 mg FP. We observed,
on average, reductions of 18% and 43% in
the MPO/total protein ratio for 0.5 mg and
2 mg FP, respectively, suggesting a dose–
response relationship.
Effects of FP on 0.25 ppm O
3
-induced
changes in surface marker expression and
phagocytosis on sputum monocytes, macro-
phages, DCs, and neutrophils. Figure 3 shows
the effect of 0.5 and 2 mg pretreatments with
FP on O
3
-induced changes in the cell-surface
markers CD11b, mCD14, CD64, CD16,
HLA-DR, and CD86 on monocytes,
macrophages, and DCs. Baseline (i.e., no O
3
exposure) sputum cell-surface marker values
(MFI; mean ± SE) from a different cohort of
healthy volunteers (n = 15) were as follows: for
CD11b, 21 ± 8 macrophages, 16 ± 3 DCs; for
mCD14, 65 ± 16 macrophages, 59 ± 14
monocytes, 61 ± 11 DCs; for CD64, 5 ± 1
monocytes; for CD16, 238 ± 44, macrophages,
195 ± 28 DCs; for HLA-DR: 31 ± 5 mono-
cytes; and for CD86, 22 ± 4 monocytes (Lay
et al. 2007). Compared with the O
3
-only con-
dition in this study (data not shown), baseline
expression of these surface markers was signifi-
cantly (p < 0.05) lower, indicating that O
3
causes an up-regulation of these cell-surface
phenotypes.
In general, 2 mg FP exerted a statistically
significant effect on post-O
3
surface marker
expression relative to placebo treatment. There
was also a similar trend after the 0.5 mg dose,
which suggests a dose–response effect of FP on
O
3
-induced changes in monocytic cell-surface
markers. We also observed a significant decrease
in CD16/FcγRIII expression on neutrophils
after 2.0 mg FP compared with placebo (MFI,
406 ± 64 vs. 515 ± 72; p < 0.05). We observed
no significant drug effect of 0.5 mg or 2 mg FP
versus placebo on sputum cells as measured by
MFI (mean ± SE): for phagocytosis for
macrophages, 478 ± 76 and 606 ± 102 versus
400 ± 50; for monocytes, 348 ± 46 and
365 ± 55 versus 292 ± 39; and for neutrophils,
296 ± 48 and 418 ± 87 versus 270 ± 29.
Effects of FP on 0.25 ppm O
3
-induced
changes in serum CCP16, SP-D, eNO, and
other systemic biomarkers. To determine
whether serum levels of the airway epithelial
cell products SP-D and CCP16 would reflect
inflammatory airway changes after O
3
expo-
sure, we measured the concentration of these
molecules at baseline and after each O
3
inhalation session in a subset of seven subjects
5 hr after O
3
exposure. Our results showed
that serum CCP16 levels were statistically sig-
nificantly increased after O
3
inhalation and
that pretreatment with 2 mg FP statistically
significantly inhibited this effect compared
with placebo (Figure 4). The effects of FP on
CCP16 were dose dependent. SP-D levels were
not statistically significantly altered pre- versus
post-O
3
exposure (mean ± SE, 61 ± 6 ng/mL
vs. 55 ± 5.4 ng/mL) and were not significantly
affected by 0.5 mg FP (53 ± 5 ng/mL) or 2 mg
FP (64 ± 5 ng/mL) compared with placebo
(55 ± 5 ng/mL).
Statistical analysis of other systemic bio-
markers or eNO yielded no clear changes
induced by O
3
exposure. No significant effects
on systemic cytokines (IL-6, IL-12P40, IL-15,
IL-17, IL-1β, IL-1Ra, INF-γ, TNF-α), medi-
ators (MPO, eotaxin), or eNO (Table 2) were
observed after 0.5 mg or 2 mg FP versus
placebo. For eNO, levels at 1, 2, and 3 hr
(Table 2) postexposure were not statistically
significantly different from one another.
Discussion
Numerous laboratory studies of healthy young
individuals exposed to O
3
at a dose compara-
ble to that used in the present study have
demonstrated decrements in spirometric lung
function (Holz et al. 1999, 2005; McDonnell
et al. 1997; Nightingale et al. 2000). A study
similar to this one in terms of the cohort char-
acteristics, O
3
concentration, and ventilation
rate also reported similar postexposure decre-
ments in FVC and FEV
1
(Holz et al. 1999).
In the present study we found that pre-
treatment with therapeutic doses of FP had no
significant protective effect on spirometric
response, which is in agreement with the
finding of Nightingale et al. (2000). FP did,
Alexis et al.
802
VOLUME 116 | NUMBER 6 | June 2008
Environmental Health Perspectives
Figure 2. The percent sputum neutrophils after O
3
exposure for each pretreatment dose of FP (0.5 or
2 mg) or placebo.
*
p
< 0.05 compared with placebo.
90
80
70
60
50
40
30
20
10
0
Placebo 0.5 mg 2 mg
*
*
Percent neutrophils
FP
Table 2. Mean (± SE) pulmonary function, eNO, and IOS.
IOS
FEV
1
(L) FVC (L) eNO (ppb) R5 X5
F
res
(Hz)
Baseline
Pretreatment 3.76 ± 0.18 4.69 ± 0.21 12.54 ± 1.55 0.376 ± 0.008 –0.112 ± 0.003 12.27 ± 0.30
Placebo
Preexposure (0 hr) 3.84 ± 0.01 4.70 ± 0.02 11.49 ± 1.26 0.409 ± 0.007 –0.161 ± 0.002 12.03 ± 0.28
Immediately after exposure 3.52 ± 0.07 4.39 ± 0.08 13.51 ± 1.39
1 hr postexposure 3.71 ± 0.05 4.60 ± 0.06 14.24 ± 1.49 0.379 ± 0.008 –0.099 ± 0.002 11.85 ± 0.27
2 hr postexposure 13.76 ± 1.43 0.404 ± 0.04 –0.102 ± 0.01 11.87 ± 1.14
3 hr postexposure 8.94 ± 1.15 0.414 ± 0.04 –0.221 ± 0.11 12.60 ± 1.38
0.5 mg FP
Preexposure (0 hr) 3.84 ± 0.02 4.75 ± 0.03 11.65 ± 1.91 0.383 ± 0.007 –0.112 ± 0.002 12.10 ± 0.24
Immediately after exposure 3.51 ± 0.05 4.43 ± 0.05 14.80 ± 1.68
1 hr postexposure 3.69 ± 0.04 4.60 ± 0.05 15.53 ± 1.70 0.356 ± 0.007 –0.106 ± 0.002 12.01 ± 0.25
2 hr postexposure 15.85 ± 1.60 0.382 ± 0.05 –0.101 ± 0.01 12.26 ± 1.43
3 hr postexposure 12.16 ± 1.2 0.393 ± 0.05 –0.196 ± 0.08 12.99 ± 1.76
2.0 mg FP
Preexposure (0 hr) 3.73 ± 0.02 4.61 ± 0.02 10.81 ± 1.75 0.382 ± 0.008 –0.113 ± 0.003 12.23 ± 0.25
Immediately after exposure 3.51 ± 0.07 4.35 ± 0.08 13.84 ± 1.32
1 hr postexposure 3.60 ± 0.04 4.41 ± 0.05 14.87 ± 1.57 0.367 ± 0.007 –0.109 ± 0.003 11.70 ± 0.24
2 hr postexposure 13.65 ± 1.18 0.365 ± 0.04 –0.099 ± 0.01 11.47 ± 1.07
3 hr postexposure 11.88 ± 1.45 0.373 ± 0.04 –0.188 ± 0.08 11.45 ± 1.07
Abbreviations: R5, total respiratory resistance (cm H
2
O/L/sec); X5, reactance (cm H
2
O/L/sec).
however, inhibit inflammatory cell (neutro-
phils, PMNs) influx to the airways induced by
a 3-hr exposure to 0.25 ppm O
3
in a dose-
dependent manner. The lack of correlation
between spirometry and airway inflammation
after O
3
has been well documented (Blomberg
et al. 1999; Hazucha et al. 1996), so our find-
ing with FP in this regard was not surprising.
We observed a significant inhibition of
the percent PMNs present in airway sputum
after O
3
challenge with either 0.5 mg or 2 mg
FP pretreatment, and a significant reduction
and a trend for reduction in the number of
sputum neutrophils per milliliter post-O
3
with 2 mg and 0.5 mg FP, respectively.
Furthermore, we showed that serum CCP16
is a valuable systemic marker of the inflam-
matory state of the lung and is responsive to
the effects of inhaled FP. We also observed
evidence of diminished neutrophil activation
with 2 mg FP, as it decreased the expression
of CD16, a marker of neutrophil activation,
compared with placebo. This observation
coincided with a reduced MPO/total protein
ratio with 2 mg FP, supporting the notion of
reduced neutrophil activation. Taken together
with previously published results (Holz et al.
2005), our results indicate that O
3
challenge
in healthy individuals is a useful model for
screening novel anti-inflammatory agents
designed for treatment of airway diseases that
have elevated neutrophils as a principal com-
ponent of their airway inflammation. These
include a subtype of severe asthma with mini-
mal airway eosinophils (Louis et al. 2000;
Wenzel 2003; Wenzel et al. 1999), as well as
COPD during an exacerbation (Hill et al.
1999; Stockley 1998).
An important feature of our study design
was that we limited volunteer recruitment to
persons with documented responsiveness to O
3
,
defined as a minimum of a 10% increase in air-
way PMNs after a screening O
3
challenge, to
enable the assessment of FP. Nightingale et al.
(2000) failed to observe an effect when they
examined the effect of 2 weeks of treatment
with 800 µg inhaled budesonide twice daily
on O
3
-induced neutrophilia in normal volun-
teers. In our study, although there was a sig-
nificant effect of O
3
alone on percent PMNs,
a substantial number of persons examined
failed to have an absolute neutrophil response
(using neutrophils per milligram sputum as a
measure) after placebo treatment. Thus, it is
possible that Nightingale et al.’s (2000) results
were influenced by a study population that
included a high proportion of O
3
“non-
responders.” In contrast, Vagaggini et al.
(2001) examined the effect of 4 weeks of pre-
treatment with 400 µg inhaled budesonide
twice daily on O
3
-induced neutrophilia in
asthmatics, and reported a significant decrease
in airway neutrophils present 6 hr after
0.27 ppm O
3
challenge compared with
placebo pretreatment; most volunteers in the
Vagaggini et al. (2001) study appeared to be
O
3
responsive. Furthermore, the objective of
the present study was not to test the efficacy of
the O
3
model, but rather to determine
whether clinically relevant doses of FP could
be assessed to support subsequent larger stud-
ies in subjects with preexisting airway disease.
In addition to its effects on airway neutro-
philia, we have recently reported that O
3
chal-
lenge (0.4 ppm, 2 hr) causes an increase in
expression of cell-surface phenotypes CD11b,
mCD14, CD16, CD86, and HLA-DR on
sputum monocytes recovered from normal
volunteers (Alexis et al. 2004a). We also
reported an increase in the numbers of spu-
tum monocytes (in addition to neutrophils),
suggesting that O
3
exposure resulted in an
influx of activated monocytes. These data are
supported by a recent animal study showing
that O
3
enhanced the expression of interstitial
lung cell-surface molecules associated with
antigen presentation and increased the number
of antigen-presenting cells in the lung (Koike
and Kobayashi 2004). In the present study,
we found that 2 mg inhaled FP decreased the
expression of CD11b, mCD14, CD16,
CD64, CD86, and HLA-DR on sputum
monocytic cells after O
3
challenge compared
with placebo treatment. The 0.5 mg dose of
FP decreased the expression of CD86 and
HLA-DR on sputum monocytes after O
3
challenge compared with placebo. Given that
these surface molecules are involved with
mediating innate immune responses (CD11b
and mCD14), acquired immune responses
(CD16, CD64), and antigen presentation
(CD86, HLA-DR), we speculate that O
3
exposure may play a role in modifying how
airway cells respond to a number of patho-
logic agents in the airborne environment. It is
unclear whether the effect of FP on O
3
-
induced changes in monocytic cell popula-
tions is due to effects on monocytes present in
the airway when exposure began, or on the
subsequent influx of monocytes that are acti-
vated from the circulation. Decreased mono-
cytic cell influx could be mediated by an effect
of FP on production of monocyte-associated
chemotactic factors or decreased adhesion
molecule expression on endothelial cells lining
the postcapillary venules.
The use of CCP16 as a systemic marker
for injury of the epithelium has been exam-
ined by several investigators (Blomberg et al.
2003; Helleday et al. 2006). O
3
exposure is
associated with increased serum levels of
CCP16 (Blomberg et al. 2003). We likewise
observed that O
3
exposure caused an increase
in serum CCP16 and further showed that
pretreatment with either 0.5 mg or 2 mg
inhaled FP prevented the O
3
-induced increase
in CCP16. We compared CCP16 with SP-D,
an innate immune molecule produced by
type II alveolar epithelial cells and Clara cells.
We previously showed that SP-D plays a
protective role in O
3
-induced injury of the
Fluticasone propionate protects against airway inflammation
Environmental Health Perspectives
VOLUME 116 | NUMBER 6 | June 2008
803
Figure 4. CCP16 levels (mean ± SE) in serum pre-O
3
and 8 hr post-O
3
for placebo and 0.5 and 2 mg FP.
*
p
< 0.05 compared with placebo.
#
p
< 0.05 for post-O
3
compared with pre-O
3
.
25
20
15
10
5
0
CCP16 (ng/mL)
Placebo
*
0.5 mg 2 mg
FP
#
Pre-O
3
Post-O
3
Figure 3. Expression (MFI; mean ± SE) of cell-surface phenotypes on sputum monocytic cells and DCs
after O
3
exposure with 0.5 mg FP, 2 mg FP, or placebo pretreatment. (
A
) CD11b/CR3. (
B
) mCD14.
(
C
) CD64/FcγRI. (
D
) CD16/FcγRIII. (
E
) HLA-DR. (
F
) CD86. Only results in which at least one dose of FP
resulted in a change in surface marker expression compared with placebo are shown.
*
p
< 0.05 for CD11b, mCD14, CD64, CD16, and CD86 compared with 2 mg FP and for HLA-DR and CD86 with compared with
0.5 mg FP.
40
30
20
10
0
MFI
Macrophages DCs
*
*
Macrophages DCsMonocytes
300
200
100
0
*
*
*
MFI
MFI
15
10
5
0
Monocytes
*
*
750
500
250
0
MFI
Macrophages
*
*
Monocytes
150
100
50
0
MFI
*
60
50
40
30
20
10
0
MFI
Monocytes
*
*
O
3
+ placebo
O
3
+ 0.5 mg FP
O
3
+ 2 mg FP
A B C
D E F
DCs
CD11b/CR3 mCD14 CD64/FcγRI
CD16/FcγRIII HLA-DR CD86
lung (Kierstein et al. 2006), but whether
release of this protein into the circulation
could parallel the inflammatory airway
changes was unclear. Our study showed that
CCP16 is a superior serum marker for injury
of the airway epithelium and is a more sensi-
tive biomarker for the effect of inhaled FP on
airway inflammation compared with SP-D or,
indeed, compared with the wide range of
cytokines, chemokines, and inflammatory
mediators we investigated.
The apparent discrepancy we observed
between serum SP-D and CCP16 was likely
influenced by many factors, including
changes in lung concentrations. We previ-
ously showed that intracellular SP-D mRNA
and protein expression are very sensitive to
corticosteroids, cAMP, and cytokine levels
(Cao et al. 2004) and that SP-D in broncho-
alveolar lavage fluid is subject to rapid break-
down after O
3
exposure of mice (Kierstein
et al. 2006). Although no formal comparisons
have been made between local (pulmonary)
expression of SP-D and CCP16, we speculate
that the CCP16 molecule is more resistant to
O
3
-induced breakdown than is SP-D. This is
supported by the fact that CCP16 serum
levels in a number of animal and human
studies accurately reflected the extent of
increases in capillary permeability after acute
exposure to lipopolysaccharide, chlorine, or
O
3
(Lakind et al. 2007; Michel et al. 2005).
Thus, the discrepancy we observed between
serum levels of SP-D and CCP16 after O
3
exposure may be due to different structure,
regulation of expression, and sensitivity to
O
3
-induced molecular changes. This discrep-
ancy highlights the specific importance of
CCP16 as a biomarker for lung injury and
treatment effectiveness.
Overall, our observations are consistent
with the hypothesis that FP will inhibit acute
airway inflammation due to O
3
exposure in a
dose-dependent fashion that includes the
therapeutic dose of 0.5 mg FP. Apart from
percent PMNs, however, several of our find-
ings with 0.5 mg FP did not reach statistical
significance. This was likely due to an insuffi-
cient number of subjects examined at this
dose. Subsequent studies using the 0.5 mg
dose of FP will require a larger sample size. It
is also possible that a more prolonged pre-
treatment with FP before O
3
challenge would
have resulted in a more pronounced effect of
0.5 mg FP on airway inflammation, but our
single-use administration of FP provided ade-
quate drug exposure over the challenge time.
We also note that this study was conducted in
normal healthy volunteers. We chose healthy
volunteers to avoid the potentially high varia-
tion in baseline inflammation associated with
subjects with preexisting airway disease.
Lower variability in healthy subjects would
reduce the need to examine a large cohort of
subjects in this study and allow us to attain an
initial proof of pharmacology for new anti-
inflammatory chemical entities. One cannot
rule out, however, that because asthmatics
have been reported to have an increased pul-
monary sensitivity to O
3
exposure (Alexis
et al. 2000b; Scannell et al. 1996), although
we did not observe a statistically significant
effect using a single administration of 0.5 mg
FP on airway inflammation, this might have
been observed in a cohort of asthmatics. As
noted above, Vagaggini et al. (2001) reported
a significant inhibition of O
3
-induced inflam-
mation in asthmatics with treatment of
400 µg budesonide administered twice daily.
Using endotoxin as an inflammatory stimu-
lus, we previously observed that 440 µg FP
for 2 weeks delivered via a metered dose
inhaler twice daily inhibited the effect of
endotoxin on neutrophilic airway inflamma-
tion in allergic asthmatics (Alexis and Peden
2001). Thus, implementation of a longer
treatment period in healthy individuals may
have resulted in demonstration of anti-
inflammatory efficacy of a single 500 µg dose
of inhaled FP.
Conclusion
We confirmed original observations that O
3
-
induced airway neutrophilic inflammation was
inhibited by a single administration of 2 mg
FP and extended the findings by demonstrat-
ing decreased neutrophilic inflammation with
the 0.5 mg FP treatment, as well. We also
observed that both doses of FP inhibited the
up-regulatory effect of O
3
on airway mono-
cytic cell-surface phenotypes and that 2 mg FP
inhibited serum levels of CCP16. Taken
together, these observations suggest that brief
treatments with inhaled corticosteroids by per-
sons in anticipation of exposure to air pol-
lution may offer protection against the
inflammatory effects of ambient air O
3
, partic-
ularly for those individuals with preexisting
airway disease. However, it is important to
note that inhaled corticosteroids had no pro-
tective effect on the spirometric decrements
induced by O
3
, suggesting this component of
airway function, particularly in individuals
with preexisting airway disease, remains sus-
ceptible to the modifying effects of O
3
expo-
sure. A second conclusion is that O
3
challenge
with subsequent analysis of airway sputum
and serum CCP16 is a good acute disease
model for phase I screening of novel anti-
inflammatory agents intended for use in
asthma and COPD.
REFERENCES
Alexis NE, Becker S, Bromberg PA, Devlin R, Peden DB. 2004a.
Circulating CD11b expression correlates with the neutro-
phil response and airway mCD14 expression is enhanced
following ozone exposure in humans. Clin Immunol
111(1):126–131.
Alexis NE, Eldridge MW, Peden DB. 2003. Effect of inhaled
endotoxin on airway and circulating inflammatory cell
phagocytosis and CD11b expression in atopic asthmatic
subjects. J Allergy Clin Immunol 112(2):353–361.
Alexis NE, Eldridge MW, Peden DB. 2004b. Effect of inhaled
endotoxin on airway and circulating inflammatory cell
phagocytosis and CD11b expression in atopic asthmatic
subjects. J Allergy Clin Immunol 12:353–361.
Alexis NE, Lay JC, Zeman K, Bennett WE, Peden DB,
Soukup JM, et al. 2006. Biological material on inhaled
coarse fraction particulate matter activates airway phago-
cytes in vivo in healthy volunteers. J Allergy Clin Immunol
117:1396–1403.
Alexis NE, Peden DB. 2001. Blunting airway eosinophilic inflam-
mation results in a decreased airway neutrophil response
to inhaled LPS in patients with atopic asthma: a role for
CD14. J Allergy Clin Immunol 108:577–580.
Alexis N, Soukup J, Ghio A, Becker S. 2000a. Sputum phagocytes
from healthy individuals are functional and activated: a
flow cytometric comparison with cells in bronchoalveolar
lavage and peripheral blood. Clin Immunol 97:21–32.
Alexis N, Urch B, Tarlo S, Corey P, Pengelly D, O’Byrne P, et al.
2000b. Cyclooxygenase metabolites play a different role in
ozone-induced pulmonary function decline in asthmatics
compared to normals. Inhal Toxicol 12(12):1205–1224.
American Thoracic Society and European Respiratory Society.
2005. Recommendations for standardized procedures for
the online and offline measurement of exhaled lower res-
piratory nitric oxide and nasal nitric oxide. Am J Respir
Crit Care Med 171(8):912–930.
Bernstein JA, Alexis N, Barnes C, Bernstein IL, Nel A, Peden D,
et al. 2004. Health effects of air pollution. J Allergy Clin
Immunol 114:1116–1123.
Blomberg A, Mudway IS, Nordenhall C, Hedenstrom H, Kelly FJ,
Frew AJ, et al. 1999. Ozone-induced lung function decre-
ments do not correlate with early airway inflammatory or
antioxidant responses. Eur Respir J 13(6):1418–1428.
Blomberg A, Mudway I, Svensson M, Hagenbjork-Gustafsson A,
Thomasson L, Helleday R, et al. 2003. Clara cell protein as a
biomarker for ozone-induced lung injury in humans. Eur
Respir J 22:883–888.
Cao Y, Tao JQ, Bates SR, Beers MF, Haczku A. 2004. IL-4
induces production of the lung collectin surfactant pro-
tein-D. J Allergy Clin Immunol 113(3):439–444.
Enright PL. 2003. How to make sure your spirometry tests are of
good quality. Respir Care 48:773–776.
Gong H, Wong R, Sarma RJ, Linn WS, Sullivan ED, Shamoo DA,
et al. Cardiovascular effects of ozone exposure in human
volunteers. 1998. Am J Respir Crit Care Med 158(2):538–546.
Haczku A. 2006. Role and regulation of lung collectins in allergic
airway sensitization. Pharmacol Ther 110(1):14–34.
Hazucha MJ, Madden M, Pape G, Becker S, Devlin R,
Koren HS, et al. 1996. Effects of cyclo-oxygenase inhibition
on ozone-induced respiratory inflammation and lung
function changes. Eur J Appl Physiol Occup Physiol
73(1–2):17–27.
Helleday R, Segerstedt B, Forsberg B, Mudway I, Nordberg G,
Bernard A, et al. 2006. Exploring the time dependence of
serum Clara cell protein as a biomarker of pulmonary
injury in humans. Chest 130:672–675.
Hill AT, Campbell EJ, Bayley DL, Hill SL, Stockley RA. 1999.
Evidence for excessive bronchial inflammation during an
acute exacerbation of chronic obstructive pulmonary dis-
ease in patients with α
1
-antitrypsin deficiency. J Respir
Crit Care Med 160:1968–1975.
Holz O, Jorres FA, Timm P, Mucke M, Richter K, Koschyk S,
et al. 1999. Ozone-induced airway inflammatory changes
differ between individuals and are reproducible. Am J
Respir Crit Care Med 159:776–784.
Holz O, Tal-Singer R, Kanniess F, Simpson KJ, Gibson A,
Vessey RS, et al. 2005. Validation of the human ozone chal-
lenge model as a tool for assessing anti-inflammatory
drugs in early development. J Clin Pharmacol 45:498–503.
Kierstein S, Poulain FR, Cao Y, Grous M, Mathias R, Kierstein G,
et al. 2006. Susceptibility to ozone-induced airway inflam-
mation is associated with decreased levels of surfactant
CORRECTION
In the original manuscript published
online, Brad Harris was not included as an
author. His name has been added here.
Alexis et al.
804
VOLUME 116 | NUMBER 6 | June 2008
Environmental Health Perspectives
Fluticasone propionate protects against airway inflammation
Environmental Health Perspectives
VOLUME 116 | NUMBER 6 | June 2008
805
protein D. Respir Res 7:85; doi:10.1186/1465-9921-7-85
[Online 1 June 2006].
Koike E, Kobayashi T. 2004. Ozone exposure enhances antigen-
presenting activity of interstitial lung cells in rats. Toxicology
196:217–227.
Lakind JS, Holgate ST, Ownby DR, Mansur AH, Helms PJ,
Pyatt D, et al. 2007. A critical review of the use of Clara
cell secretory protein (CC16) as a biomarker of acute or
chronic pulmonary effects. Biomarkers 12(5):445–467.
Lay JC, Alexis NE, Kleeberger SR, Roubey RAS, Harris BD,
Bromberg PA, et al. 2007. Ozone exposure enhances expres-
sion of surface markers of innate immunity and antigen pre-
sentation on airway monocytes in healthy individuals.
J Allergy Clin Immunol 120(3):719–722.
Louis R, Lau LCK, Bron AO, Roldaan AC, Radermecker M,
Djukanovi R. 2000. The relationship between airways
inflammation and asthma severity. Am J Respir Crit Care
Med 161:9–16.
Maneechotesuwan K, Essilfie-Quaye S, Kharitonov SA,
Adcock IM, Barnes PJ. 2007. Loss of control of asthma fol-
lowing inhaled corticosteroid withdrawal is associated
with increased sputum interleukin-8 and neutrophils. Chest
132(1):98–105.
McDonnell WF, Stewart PW, Andreoni S, Seal E Jr, Kehrl HR,
Horstman DH, et al. 1997. Prediction of ozone-induced
FEV
1
changes. Effects of concentration, duration, and ven-
tilation. Am J Respir Crit Care Med 156:715–722.
Michel O, Murdoch R, Bernard A. 2005. Inhaled LPS induces
blood release of Clara cell specific protein (CC16) in human
beings. J Allergy Clin Immunol 115:1143–1147.
Nightingale JA, Rogers DF, Fan CK, Barnes PJ. 2000. No effect
of inhaled budesonide on the response to inhaled ozone in
normal subjects. Am J Respir Crit Care Med 161:479–486.
Pauwels RA. 2004. Similarities and differences in asthma and
chronic obstructive pulmonary disease exacerbations.
Proc Am Thorac Soc 1(2):73–76.
Peden DB. 2001. Air pollution in asthma: effect of pollutants on
airway inflammation. Ann Allergy Asthma Immunol 87:12–17.
Scannell C, Chen L, Aris RM, Tager I, Christian D, Ferrando R,
et al. 1996. Greater ozone-induced inflammatory responses
in subjects with asthma. Am J Respir Crit Care Med
154(1):24–29.
Singh R, Tal-Singer R, Faiferman I, Lasenby S, Henderson A,
Wessels D, et al. 2006. Plethysmography and impulse
oscillometry assessment of tiotropium and ipratropium
bromide; a randomised, double blind, placebo controlled,
crossover study in healthy subjects. Br J Clin Pharm
61(4):398–404.
Stockley RA. 1998. Role of bacteria in the pathogenesis and
progression of acute and chronic lung infection. Thorax
53:58–62.
Vagaggini B, Taccola M, Conti I, Carnevali S, Cianchetti S,
Bartoli ML, et al. 2001. Budesonide reduces neutrophilic but
not functional airway response to ozone in mild asthmatics.
Am J Respir Crit Care Med 164:2172–2176.
Wenzel S. 2003. Severe/fatal asthma. Chest 123:405S–410S.
Wenzel SE, Schwartz LB, Langmack EL, Halliday JL,
Trudeau JB, Gibbs RL, et al. 1999. Evidence that severe
asthma can be divided pathologically into two inflamma-
tory subtypes with distinct physiologic and clinical charac-
teristics. Am J Respir Crit Care Med 160:1001–1008.
... This protocol was developed to screen and identify volunteers who demonstrate inflammatory responsiveness to WSP for their entry into subsequent early phase studies of candidate mitigation interventions for WSP-induced airways inflammation. This approach was modeled on screening protocols developed by Holz, et al (Holz et al. 2005) and employed by our group (Alexis et al. 2008) to identify inflammatory responders, that is, persons who had a >10% increase in sputum neutrophils (PMN) post O3 for recruitment into studies evaluating anti-inflammatory interventions for O3. These placebo-controlled studies of recruited O3 inflammatory responders demonstrated that inhaled fluticasone (Holz et al. 2005;Alexis et al. 2008) and oral prednisolone (Holz et al. 2005) reduced O3 induced airway inflammation. ...
... This approach was modeled on screening protocols developed by Holz, et al (Holz et al. 2005) and employed by our group (Alexis et al. 2008) to identify inflammatory responders, that is, persons who had a >10% increase in sputum neutrophils (PMN) post O3 for recruitment into studies evaluating anti-inflammatory interventions for O3. These placebo-controlled studies of recruited O3 inflammatory responders demonstrated that inhaled fluticasone (Holz et al. 2005;Alexis et al. 2008) and oral prednisolone (Holz et al. 2005) reduced O3 induced airway inflammation. The advantage of excluding non-responsive volunteers from these intervention studies, was to improve study efficiency and eliminate uninformative data from O3 non-responsive volunteers. ...
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Background: We are currently screening human volunteers to determine their sputum polymorphonuclear neutrophil (PMN) response 6- and 24-hours following initiation of exposure to wood smoke particles (WSP). Inflammatory responders (≥10% increase in %PMN) are identified for their subsequent participation in mitigation studies against WSP-induced airways inflammation. In this report we compared responder status (N = 52) at both 6 and 24 hr time points to refine/expand its classification, assessed the impact of the GSTM1 genotype, asthma status and sex on responder status, and explored whether sputum soluble phase markers of inflammation correlate with PMN responsiveness to WSP. Results: Six-hour responders tended to be 24-hour responders and vice versa, but 24-hour responders also had significantly increased IL-1beta, IL-6, IL-8 at 24 hours post WSP exposure. The GSTM1 null genotype significantly (p < 0.05) enhanced the %PMN response by 24% in the 24-hour responders and not at all in the 6 hours responders. Asthma status enhanced the 24 hour %PMN response in the 6- and 24-hour responders. In the entire cohort (not stratified by responder status), we found a significant, but very small decrease in FVC and systolic blood pressure immediately following WSP exposure and sputum %PMNs were significantly increased and associated with sputum inflammatory markers (IL-1beta, IL-6, IL-8, and PMN/mg) at 24 but not 6 hours post exposure. Blood endpoints in the entire cohort showed a significant increase in %PMN and PMN/mg at 6 but not 24 hours. Sex had no effect on %PMN response. Conclusions: The 24-hour time point was more informative than the 6-hour time point in optimally and expansively defining airway inflammatory responsiveness to WSP exposure. GSTM1 and asthma status are significant effect modifiers of this response. These study design and subject parameters should be considered before enrolling volunteers for proof-of-concept WSP mitigation studies.
... Release of alarmins and influx of inflammatory cells into the airways are the pathological hallmark of severe asthma exacerbations (2,5,10,14). In the healthy lung, the primary inflammatory cells recruited to the airways following O 3 inhalation are the neutrophilic granulocytes (147,148). These cells appear in the airways within minutes and accumulate in significant numbers as early as 1-2 h after exposure (89,106,149). ...
... These cells appear in the airways within minutes and accumulate in significant numbers as early as 1-2 h after exposure (89,106,149). In healthy human subjects exposed to O 3 under experimental conditions, a significant airway neutrophilia was associated with a decrease in lung function (7,147,150) indicating the pathological significance of these cells. Interestingly, when O 3 exposure is combined with allergic sensitization in mouse models, asthmatic non-human primates (rhesus macaques) and in allergic human subjects, a marked influx of both eosinophilic and neutrophilic granulocytes is observed (10,94,101,106). ...
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Despite recent advances in using biologicals that target Th2 pathways, glucocorticoids form the mainstay of asthma treatment. Asthma morbidity and mortality remain high due to the wide variability of treatment responsiveness and complex clinical phenotypes driven by distinct underlying mechanisms. Emerging evidence suggests that inhalation of the toxic air pollutant, ozone, worsens asthma by impairing glucocorticoid responsiveness. This review discusses the role of oxidative stress in glucocorticoid resistance in asthma. The underlying mechanisms point to a central role of oxidative stress pathways. The primary data source for this review consisted of peer-reviewed publications on the impact of ozone on airway inflammation and glucocorticoid responsiveness indexed in PubMed. Our main search strategy focused on cross-referencing “asthma and glucocorticoid resistance” against “ozone, oxidative stress, alarmins, innate lymphoid, NK and γδ T cells, dendritic cells and alveolar type II epithelial cells, glucocorticoid receptor and transcription factors”. Recent work was placed in the context from articles in the last 10 years and older seminal research papers and comprehensive reviews. We excluded papers that did not focus on respiratory injury in the setting of oxidative stress. The pathways discussed here have however wide clinical implications to pathologies associated with inflammation and oxidative stress and in which glucocorticoid treatment is essential.
... Inhalation of O 3 , an ubiquitous, oxidizing, and toxic air pollutant induces acute exacerbations with proinflammatory mediator release, neutrophilic granulocyte influx and obstruction of airways (9)(10)(11)(12)(13)(14)(15) and substantially worsens asthma morbidity and mortality (16,17). Data obtained from studies on mice (18), dogs (19) rhesus macaques (20), healthy volunteers (21), and asthma patients (22,23) have been controversial on whether glucocorticoids are effective to inhibit O 3 -induced exacerbation of airway inflammation and airway hyperreactivity in asthma. Further, the mechanisms of increased susceptibility of the asthmatic airways to O 3 and how glucocorticoid action is affected by inhalation of this air pollutant remain unclear. ...
... Inhaled glucocorticoids are currently the main choice for asthma treatment because they can profoundly improve lung function, alleviate airway inflammation and airway hyperreactivity (1, 48, 49) but their effectiveness in acute asthma exacerbations is subject of on-going debate (49-51, 58-60). Studies on asthma exacerbations caused by exposure to air pollutants are limited (61,62) and the available experimental data on animals (18)(19)(20) and humans (21)(22)(23) are unclear on whether inhaled corticosteroids are effective to treat O 3induced airway inflammation and/or airway hyperreactivity in asthma. We wanted therefore to further investigate the effects of budesonide on O 3 -induced exacerbation of allergic airway changes. ...
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Inhaled glucocorticoids form the mainstay of asthma treatment because of their anti-inflammatory effects in the lung. Exposure to the air pollutant ozone (O3) exacerbates chronic airways disease. We and others showed that presence of the epithelial-derived surfactant protein-D (SP-D) is important in immunoprotection against inflammatory changes including those induced by O3 inhalation in the airways. SP-D synthesis requires glucocorticoids. We hypothesized here that O3 exposure impairs glucocorticoid responsiveness (including SP-D production) in allergic airway inflammation. The effects of O3 inhalation and glucocorticoid treatment were studied in a mouse model of allergic asthma induced by sensitization and challenge with Aspergillus fumigatus (Af) in vivo. The role of O3 and glucocorticoids in regulation of SP-D expression was investigated in A549 and primary human type II alveolar epithelial cells in vitro. Budesonide inhibited airway hyperreactivity, eosinophil counts in the lung and bronchoalveolar lavage (BAL) and CCL11, IL-13, and IL-23p19 release in the BAL of mice sensitized and challenged with Af (p < 0.05). The inhibitory effects of budesonide were attenuated on inflammatory changes and were completely abolished on airway hyperreactivity after O3 exposure of mice sensitized and challenged with Af. O3 stimulated release of pro-neutrophilic mediators including CCL20 and IL-6 into the airways and impaired the inhibitory effects of budesonide on CCL11, IL-13 and IL-23. O3 also prevented budesonide-induced release of the immunoprotective lung collectin SP-D into the airways of allergen-challenged mice. O3 had a bi-phasic direct effect with early (<12 h) inhibition and late (>48 h) activation of SP-D mRNA (sftpd) in vitro. Dexamethasone and budesonide induced sftpd transcription and translation in human type II alveolar epithelial cells in a glucocorticoid receptor and STAT3 (an IL-6 responsive transcription factor) dependent manner. Our study indicates that O3 exposure counteracts the effects of budesonide on airway inflammation, airway hyperreactivity, and SP-D production. We speculate that impairment of SP-D expression may contribute to the acute O3-induced airway inflammation. Asthmatics exposed to high ambient O3 levels may become less responsive to glucocorticoid treatment during acute exacerbations.
... O 3 responder status was based on previously reported criteria for a robust pro-inflammatory O 3 response based on a >10% increase in post vs pre-exposure (%Neutrophils Post-% Neutrophils Pre) [54]. To determine if plasma sterol concentrations could be utilized for predicting O 3 responsiveness, machine learning models were constructed using all subjects. ...
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Background: Ozone (O3) exposure causes respiratory effects including lung function decrements, increased lung permeability, and airway inflammation. Additionally, baseline metabolic state can predispose individuals to adverse health effects from O3. For this reason, we conducted an exploratory study to examine the effect of O3 exposure on derivatives of cholesterol biosynthesis: sterols, oxysterols, and secosteroid (25-hydroxyvitamin D) not only in the lung, but also in circulation. Methods: We obtained plasma and induced sputum samples from non-asthmatic (n = 12) and asthmatic (n = 12) adult volunteers 6 hours following exposure to 0.4ppm O3 for 2 hours. We quantified the concentrations of 24 cholesterol precursors and derivatives by UPLC-MS and 30 cytokines by ELISA. We use computational analyses including machine learning to determine whether baseline plasma sterols are predictive of O3 responsiveness. Results: We observed an overall decrease in the concentration of cholesterol precursors and derivatives (e.g. 27-hydroxycholesterol) and an increase in concentration of autooxidation products (e.g. secosterol-B) in sputum samples. In plasma, we saw a significant increase in the concentration of secosterol-B after O3 exposure. Machine learning algorithms showed that plasma cholesterol was a top predictor of O3 responder status based on decrease in FEV1 (>5%). Further, 25-hydroxyvitamin D was positively associated with lung function in non-asthmatic subjects and with sputum uteroglobin, whereas it was inversely associated with sputum myeloperoxidase and neutrophil counts. Conclusion: This study highlights alterations in sterol metabolites in the airway and circulation as potential contributors to systemic health outcomes and predictors of pulmonary and inflammatory responsiveness following O3 exposure.
... Corticosteroids can attenuate the single exposure effects of ozone including AHR and lung inflammation (95)(96)(97). This includes the inhibition of expression of macrophage inflammatory protein 2 (MIP-2), inducible nitric oxidase synthase (iNOS) (98,99) and NFκB (96), and the increased proliferation of the airway epithelium (91). ...
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Oxidative stress plays an important role in the pathogenesis of chronic obstructive pulmonary disease (COPD) caused by cigarette smoke and characterized by chronic inflammation, alveolar destruction (emphysema) and bronchiolar obstruction. Ozone is a gaseous constituent of urban air pollution resulting from photochemical interaction of air pollutants such as nitrogen oxide and organic compounds. While acute exposure to ozone induces airway hyperreactivity and neutrophilic inflammation, chronic ozone exposure in mice causes activation of oxidative pathways resulting in cell death and a chronic bronchial inflammation with emphysema, mimicking cigarette smoke-induced COPD. Therefore, the chronic exposure to ozone has become a model for studying COPD. We review recent data on mechanisms of ozone induced lung disease focusing on pathways causing chronic respiratory epithelial cell injury, cell death, alveolar destruction, and tissue remodeling associated with the development of chronic inflammation and AHR. The initial oxidant insult may result from direct effects on the integrity of membranes and organelles of exposed epithelial cells in the airways causing a stress response with the release of mitochondrial reactive oxygen species (ROS), DNA, and proteases. Mitochondrial ROS and mitochondrial DNA activate NLRP3 inflammasome and the DNA sensors cGAS and STING accelerating cell death pathways including caspases with inflammation enhancing alveolar septa destruction, remodeling, and fibrosis. Inhibitors of mitochondrial ROS, NLRP3 inflammasome, DNA sensor, cell death pathways, and IL-1 represent novel therapeutic targets for chronic airways diseases underlined by oxidative stress.
... 16 Mice lacking SP-D had increased numbers of CD4 + lymphocytes with elevated IL-13 and thymus-and activation-regulated chemokine levels in the lung and showed exaggerated production of IgE and IgG1 following allergic sensitization. 16 Further, exposure of mice 17 or human volunteers 19 to O 3 also induced SP-D expression in the lung and in the circulation, respectively. SP-D induction was mediated by IL-6 in type II alveolar epithelial cells. ...
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The asthmatic airways are highly susceptible to inflammatory injury by air pollutants such as ozone (O3), characterized by enhanced activation of eosinophilic granulocytes and a failure of immune protective mechanisms. Eosinophil activation during asthma exacerbation contributes to the proinflammatory oxidative stress by high levels of nitric oxide (NO) production and extracellular DNA release. Surfactant protein-D (SP-D), an epithelial cell product of the airways, is a critical immune regulatory molecule with a multimeric structure susceptible to oxidative modifications. Using recombinant proteins and confocal imaging, we demonstrate here that SP-D directly bound to the membrane and inhibited extracellular DNA trap formation by human and murine eosinophils in a concentration and carbohydrate-dependent manner. Combined allergic airway sensitization and O3 exposure heightened eosinophilia and nos2 mRNA (iNOS) activation in the lung tissue and S-nitrosylation related de-oligomerisation of SP-D in the airways. In vitro reproduction of the iNOS action led to similar effects on SP-D. Importantly, S-nitrosylation abolished the ability of SP-D to block extracellular DNA trap formation. Thus, the homeostatic negative regulatory feedback between SP-D and eosinophils is destroyed by the NO-rich oxidative lung tissue environment in asthma exacerbations. Demonstration that specific carbohydrate-dependent inhibition of murine and human eosinophil extracellular DNA trap release is abolished by s-nitrosylation of the SP-D molecule.
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Particular matter (PM) exposure is a big hazard for public health, especially for children. Serum CC16 is a well-known biomarker of respiratory health. Urinary CC16 (U-CC16) can be a noninvasive alternative, albeit requiring adequate adjustment for renal handling. Moreover, the SNP CC16 G38A influences CC16 levels. This study aimed to monitor the effect of short-term PM exposure on CC16 levels, measured noninvasively in schoolchildren, using an integrative approach. We used a selection of urine and buccal DNA samples from 86 children stored in an existing biobank. Using a multiple reaction monitoring method, we measured U-CC16, as well as RBP4 (retinol-binding-protein-4) and β2M (beta-2-microglobulin), required for adjustment. Buccal DNA samples were used for CC16 G38A genotyping. Linear mixed-effects models were used to find relevant associations between U-CC16 and previously obtained data from recent daily PM ≤ 2.5 or 10 μm exposure (PM2.5, PM10) modeled at the child's residence. Our study showed that exposure to low PM at the child's residence (median levels 18.9 μg/m³ (PM2.5) and 23.6 μg/m³ (PM10)) one day before sampling had an effect on the covariates-adjusted U-CC16 levels. This effect was dependent on the CC16 G38A genotype, due to its strong interaction with the association between PM levels and covariates-adjusted U-CC16 (P = 0.024 (PM2.5); P = 0.061 (PM10)). Only children carrying the 38 GG genotype showed an increase of covariates-adjusted U-CC16, measured 24h after exposure, with increasing PM2.5 and PM10 (β = 0.332; 95% CI: 0.110 to 0.554 and β = 0.372; 95% CI: 0.101 to 0.643, respectively). To the best of our knowledge, this is the first study using an integrative approach to investigate short-term PM exposure of children, using urine to detect early signs of pulmonary damage, and taking into account important determinants such as the genetic background and adequate adjustment of the measured biomarker in urine.
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Background Neighborhood poverty has been associated with poor health outcomes. Previous studies have also identified adverse respiratory effects of long-term ambient ozone. Factors associated with neighborhood poverty may accentuate the adverse impact of ozone on respiratory health. Objectives To evaluate whether neighborhood poverty modifies the association between ambient ozone exposure and respiratory morbidity including symptoms, exacerbation risk, and radiologic parameters, among participants of the SPIROMICS AIR cohort study. Methods Spatiotemporal models incorporating cohort-specific monitoring estimated 10-year average outdoor ozone concentrations at participants' homes. Adjusted regression models were used to determine the association of ozone exposure with respiratory outcomes, accounting for demographic factors, education, individual income, body mass index (BMI), and study site. Neighborhood poverty rate was defined by percentage of families living below federal poverty level per census tract. Interaction terms for neighborhood poverty rate with ozone were included in covariate-adjusted models to evaluate for effect modification. Results 1874 participants were included in the analysis, with mean (± SD) age 64 (± 8.8) years and FEV1 (forced expiratory volume in one second) 74.7% (±25.8) predicted. Participants resided in neighborhoods with mean poverty rate of 9.9% (±10.3) of families below the federal poverty level and mean 10-year ambient ozone concentration of 24.7 (±5.2) ppb. There was an interaction between neighborhood poverty rate and ozone concentration for numerous respiratory outcomes, including COPD Assessment Test score, modified Medical Research Council Dyspnea Scale, six-minute walk test, and odds of COPD exacerbation in the year prior to enrollment, such that adverse effects of ozone were greater among participants in higher poverty neighborhoods. Conclusion Individuals with COPD in high poverty neighborhoods have higher susceptibility to adverse respiratory effects of ambient ozone exposure, after adjusting for individual factors. These findings highlight the interaction between exposures associated with poverty and their effect on respiratory health.
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Increased adverse health effects in older subjects due to exposure to ambient air pollutants may be related to the inflammatory response induced by these contaminants. The aim of this study was to assess airway and systemic inflammatory responses in older healthy subjects to a controlled experimental exposure with spark-generated elemental carbon black ultrafine particles (cbUFPs) and ozone (O3). Twenty healthy subjects, age 52–75 years, were exposed on three occasions separated by at least 8 weeks. The exposures to filtered air (FA), to cbUFP (50 μg/m³), or to cbUFP in combination with 250 ppb ozone (cbUFP + O3) for 3 h with intermittent exercise were performed double blind, and in random order. Sputum and blood samples were collected 3.5 h after each exposure. Exposure to cbUFP + O3 significantly increased plasma club cell protein 16 (CC16), the number of sputum cells, the number and percent of sputum neutrophils, and sputum interleukin 6 and matrix metalloproteinase 9. Exposure to cbUFP alone exerted no marked effect, except for an elevation in sputum neutrophils in a subgroup of 13 subjects that displayed less than 65% sputum neutrophils after FA exposure. None of the inflammatory markers was correlated with age, and serum cardiovascular risk markers were not markedly affected by cbUFP or cbUFP + O3. Exposure to cbUFP+O3 induced a significant airway and systemic inflammatory response in older healthy volunteer subjects. The effects induced by cbUFP alone suggest that the inflammation was predominantly mediated by O3, although one cannot rule out that the interaction of cbUFP and O3 played a role.
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The mechanisms associated with the development of severe, corticosteroid (CS)-dependent asthma are poorly understood, but likely heterogenous. It was hypothesized that severe asthma could be divided pathologically into two inflammatory groups based on the presence or absence of eosinophils, and that the inflammatory subtype would be associated with distinct structural, physiologic, and clinical characteristics. Thirty-four severe, refractory CS-dependent asthmatics were evaluated with endobronchial biopsy, pulmonary function, allergy testing, and clinical history. Milder asthmatic and normal control subjects were also evaluated. Tissue cell types and subbasement membrane (SBM) thickness were evaluated immunohistochemically. Fourteen severe asthmatics [eosinophil (-)] had nearly absent eosinophils (< 2 SD from the normal mean). The remaining 20 severe asthmatics were categorized as eosinophil (+). Eosinophil (+) severe asthmatics had associated increases (p < 0.05) in lymphocytes (CD3+, CD4+, CD8+), mast cells, and macrophages. Neutrophils were increased in severe asthmatics and not different between the groups. The SBM was significantly thicker in eosinophil (+) severe asthmatics than eosinophil (-) severe asthmatics and correlated with eosinophil numbers (r = 0.50). Despite the absence of eosinophils and the thinner SBM, the FEV(1) was marginally lower in eosinophil (-) asthmatics (p = 0.05) with no difference in bronchodilator response. The eosinophil (+) group (with a thicker SBM) had more intubations than the eosinophil (-) group (p = 0.0004). Interestingly, this group also had a decreased FVC/slow vital capacity (SVC). These results suggest that two distinct pathologic, physiologic, and clinical subtypes of severe asthma exist, with implications for further research and treatment.
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The general public, especially patients with upper or lower respiratory symptoms, is aware from media reports that adverse respiratory effects can occur from air pollution. It is important for the allergist to have a current knowledge of the potential health effects of air pollution and how they might affect their patients to advise them accordingly. Specifically, the allergist-clinical immunologist should be keenly aware that both gaseous and particulate outdoor pollutants might aggravate or enhance the underlying pathophysiology of both the upper and lower airways. Epidemiologic and laboratory exposure research studies investigating the health effects of outdoor air pollution each have advantages and disadvantages. Epidemiologic studies can show statistical associations between levels of individual or combined air pollutants and outcomes, such as rates of asthma, emergency visits for asthma, or hospital admissions, but cannot prove a causative role. Human exposure studies, animal models, and tissue or cellular studies provide further information on mechanisms of response but also have inherent limitations. The aim of this rostrum is to review the relevant publications that provide the appropriate context for assessing the risks of air pollution relative to other more modifiable environmental factors in patients with allergic airways disease.
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In order to test the hypothesis that ozone (O3)-induced changes in lung function and respiratory tract injury/inflammation are greater in subjects with asthma than in normal subjects, we exposed 18 asthmatic subjects, on separate days, to O3 (0.2 ppm) and filtered air for 4 h during exercise. Symptom questionnaires were administered before and after exposure, and pulmonary function tests (FEV1, FVC, and specific airway resistance [SRaw]) were performed before, during, and immediately after each exposure. Fiberoptic bronchoscopy, with proximal airway lavage (PAL) of the isolated left main bronchus and bronchoalveolar lavage (BAL; bronchial fraction, the first 10 ml of fluid recovered) of the right middle lobe, was performed 18 h after each exposure. The PAL, bronchial fraction, and BAL fluids were analyzed for the following endpoints: total and differential cell counts; total protein, lactate dehydrogenase (LDH), fibronectin, interleukin-8 (IL-8), granulocyte-macrophage colony-stimulating factor (GM-CSF), myeloperoxidase (MPO), and transforming growth factor-beta (TGF beta 2) concentrations. We found a significant O3 effect on FEV1, FVC, SRaw (p < 0.04) and lower respiratory symptoms (p < 0.001) for the asthmatic subjects. Ozone exposure also significantly increased the percent neutrophils in PAL (p < 0.01); percent neutrophils, total protein, and IL-8 in the bronchial fraction (p < 0.001, p < 0.05, and p < 0.01, respectively); and the percent neutrophils, total protein, LDH, fibronectin, IL-8, GM-CSF, and MPO in BAL (p < 0.001, p < 0.01, p < 0.01, p < 0.001, p < 0.05, p < 0.01, and p < 0.001, respectively) for the asthmatic subjects. There were no significant differences in the lung function responses of the asthmatic subjects in comparison with a group of normal subjects (n = 81) previously studied using an identical protocol, although there was a trend toward a greater O3-induced increase in SRaw in the asthmatic subjects (p < 0.13). In contrast, the asthmatic subjects showed significantly greater (p < 0.05) O3-induced increases in several inflammatory endpoints (percent neutrophils and total protein concentration) in BAL as compared with normal subjects who underwent bronchoscopy (n = 20). Our results indicate that asthmatic persons may be at risk of developing more severe O3-induced respiratory tract injury/inflammation than normal persons, and may help explain the increased asthma morbidity associated with O3 pollution episodes observed in epidemiologic studies.
Inhalation of O3 causes airways neutrophilic inflammation accompanied by other changes including increased levels of cyclo-oxygenase products of arachidonic acid in bronchoalveolar lavage fluid (BALF). Ozone O3 exposure also causes decreased forced vital capacity (FVC) and forced expiratory volume after 1 s (FEV(1)), associated with cough and substernal pain on inspiration, and small increases in specific airway resistance (SRAW). The spirometric decrements are substantially blunted by pretreatment with indomethacin. Since the O3-induced decrement in FVC is due to involuntary inhibition of inspiration, a role for stimulation of nociceptive respiratory tract afferents has been suggested and cyclo-oxygenase products have been hypothesized to mediate this stimulation. However, the relation (if any) between the O3-induced neutrophilic airways inflammation and decreased inspiratory capacity remains unclear. We studied the effects of pharmacologic inhibition of O3-induced spirometric changes on the inflammatory changes. Each of ten healthy men was exposed twice (5-week interval) to 0.4 ppm O3 for 2 h, including 1 h of intermittent exercise (ventilation 601*min(-1)). One-and-a-half hours prior to and midway during each exposure the subject ingested 800 mg and 200 mg, respectively, of the non-steroidal anti-inflammatory drug ibuprofen (IBU), or placebo [PLA (sucrose)], in randomized, double-blind fashion. Spirometry and body plethysmography were performed prior to drug administration, and before and after O3 exposure. Immediately following postexposure testing, fiberoptic bronchoscopy with bronchoalveolar lavage (BAL) was performed. Neither IBU nor PLA administration changed pre-exposure lung function. O3 exposure (with PLA) caused a significant 17 percent mean decrement in FEV(1) (P <0.01) and a 56 percent increase in mean SRAW. Following IBU pretreatment, O3 exposure induced a significantly lesser mean decrement in FEV(1) (7 percent) but still a 50 percent increase in mean SRAW. IBU pretreatment significantly decreased post-O3 BAL levels of prostaglandin E2 (PGE2) by 60.4 percent (P <0.05) and thromboxane B(2) (TxB(2)) by 25.5 percent (P <0.05). Of the proteins, only interleukin-6 was significantly reduced (45 percent, P <0.05) by IBU as compared to PLA pretreatment. As expected, O3 exposure produced neutrophilia in BALF. There was, however, no effect of IBU on this finding. None of the major cell types in the BALF differed significantly between pretreatments. We found no association between post-exposure changes of BALF components and pulmonary function decrements. We conclude that IBU causes significant inhibition of O3-induced increases in respiratory tract PGE(2) and TxB(2) levels concomitant with a blunting of the spirometric response. This is consistent with the hypothesis that the products of AA metabolism mediate inhibition of inspiration. However, IBU did not alter the modest SRAW response to O3.
Article
The purpose of this analysis of previously published data was to identify a model that accurately predicts the mean ozone-induced FEV1 response of humans as a function of concentration (C), minute ventilation (VE), duration of exposure (T), and age. Healthy young adults (n = 485) were exposed for 2 h to one of six ozone concentrations while exercising at one of three levels. Candidate models were fitted to portions of the data and evaluated on the basis of their ability to predict the mean response of independent samples. A sigmoid-shaped model that is consistent with previous observations of ozone exposure-response (E-R) characteristics was identified and found to accurately predict the mean response with independent data. This model in a more general form may allow the prediction of responses under conditions of changing C and VE. We did not find that response was more sensitive to changes in C than in VE, nor did we find convincing evidence of an effect of body size upon response. We did find that response to ozone decreases with age. In summary, we have identified a biologically plausible, predictive model that quantifies the relationship between the ozone-induced change in FEV1, and C, VE, T, and age.
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We hypothesized that ozone (O3) exposure acutely affects cardiovascular hemodynamics in humans and, in particular, in subjects with essential hypertension. We studied 10 nonmedicated hypertensive and six healthy male adults. Each subject, after catheterization of the right heart and a radial artery, was exposed in an environmentally controlled chamber to filtered air (FA) on one day and to 0.3 ppm O3 on the following day for 3 h with intermittent exercise. Relative to FA exposure, O3 exposure induced no statistically significant changes in cardiac index, ventricular performance, pulmonary artery pressure, pulmonary and systemic vascular resistances, ECG, serum cardiac enzymes, plasma catecholamines and atrial natriuretic factor, and SaO2. The overall results did not indicate major acute cardiovascular effects of O3 in either the hypertensive or the control subjects. However, mean preexposure to postexposure changes were significantly (p < 0.02) larger with O3 than with FA for rate-pressure product (1,353 beats/min/mm Hg) and for heart rate (8 beats/min); these responses were not significantly different between the hypertensive and the control subjects. Significant O3 effects were also observed for mean FEV1 (-6%), and AaPO2 (> 10 mm Hg increase), which were not significantly different between the two groups. These results suggest that O3 exposure can increase myocardial work and impair pulmonary gas exchange to a degree that might be clinically important in persons with significant preexisting cardiovascular impairment, with or without concomitant lung disease.
Article
To study whether the individual inflammatory response to ozone was reproducible, dose-dependent, and time-dependent, we performed two exposures to 250 ppb ozone, one to 125 ppb and one to filtered air, each for 3 h of intermittent exercise and separated by at least 1 wk. Twenty-one healthy and 15 asthmatic subjects participated in the study. One hour after the two exposures to 250 ppb ozone we observed a mean increase in sputum neutrophils of 17.9 and 17.9% in healthy and of 20.3 and 15.2% in asthmatic subjects (p < 0.05 each). Twenty-four hours after exposure, the respective values were 11.9 and 14.8%, and 9.1 and 16.1% (p < 0.05 each). In the whole group of subjects, individual changes in the percentage of neutrophils were significantly correlated between the two exposure days 1 h (r = 0.87, p < 0.001; intraclass correlation coefficient [Ri] = 0.86) as well as 24 h (r = 0.79, p < 0.001; Ri = 0.71) after exposure. The percentages of lymphocytes were increased 24 h after exposures (all subjects combined: p < 0.05). The decrease in FEV1 in both groups (p < 0.01), was also reproducible (r = 0.77, p < 0.001), but there were no correlations between changes in sputum parameters and lung function. Exposure to 125 ppb ozone caused a small increase (p < 0. 05) in the percentage of neutrophils in asthmatic subjects and in the concentrations of interleukin-8 in both groups combined. Our data demonstrate that inflammatory and lung function responses to ozone differ between individuals and are reproducible but not related to each other. Therefore, these responses appear to represent two independent factors underlying the airway response to ozone.
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This study sought to clarify the early events occurring within the airways of healthy human subjects performing moderate intermittent exercise following ozone challenge. Thirteen healthy nonsmoking subjects were exposed in a single blinded, crossover control fashion to 0.2 parts per million (ppm) O3 and filtered air for 2 h, using a standard intermittent exercise and rest protocol. Lung function was assessed pre- and immediately post-exposure. Bronchoscopy was performed with endobronchial mucosal biopsies, bronchial wash (BW) and bronchoalveolar lavage (BAL) 1.5 h after the end of the exposure period. Respiratory tract lining fluid (RTLF) redox status was assessed by measuring a range of antioxidants and oxidative damage markers in BW and BAL fluid samples. There was a significant upregulation after O3 exposure in the expression of vascular endothelial P-selectin (p<0.005) and intercellular adhesion molecule-1 (p<0.005). This was associated with a 2-fold increase in submucosal mast cells (p<0.005) in biopsy samples, without evidence of neutrophilic inflammation, and a decrease in BAL fluid macrophage numbers (1.6-fold, p<0.005), with an activation of the remaining macrophage subset (2.5-fold increase in % human leukocyte antigen (HLA)-DR+ cells, p<0.005). In addition, exposure led to a 4.5-fold and 3.1-fold increase of reduced glutathione (GSH) concentrations, in BW and BAL fluid respectively (p<0.05), with alterations in urate and alpha-tocopherol plasma/RTLF partitioning ratios (p<0.05). Spirometry showed reductions in forced vital capacity (p<0.05) and forced expiratory volume in one second (p<0.01), with evidence of small airway narrowing using forced expiratory flow values (p<0.005). Evidence was found of O3-induced early adhesion molecule upregulation, increased submucosal mast cell numbers and alterations to the respiratory tract lining fluid redox status. No clear relationship was demonstrable between changes in these early markers and the lung function decrements observed. The results therefore indicate that the initial lung function decrements are not predictive of, or causally related to the O3-induced inflammatory events in normal human subjects.
Article
Patients with homozygous (PiZ) alpha(1)-antitrypsin (AAT) deficiency have not only low baseline serum AAT levels (approximately 10 to 15% normal) but also an attenuated acute phase response. They are susceptible to the development of premature emphysema but may also be particularly susceptible to lung damage during bacterial exacerbations when there will be a significant neutrophil influx. The purposes of the present study were to assess the inflammatory nature of acute bacterial exacerbations of chronic obstructive pulmonary disease (COPD) in subjects with AAT deficiency, to compare this with COPD patients without deficiency, and to monitor the inflammatory process and its resolution following appropriate antibacterial therapy. At the start of the exacerbation, patients with AAT deficiency had lower sputum AAT (p < 0.001) and secretory leukoprotease inhibitor (SLPI; p = 0.02) with higher elastase activity (p = 0.02) compared with COPD patients without deficiency. Both groups had a comparable acute phase response as assessed by C-reactive protein (CRP) but the AAT-deficient patients had a minimal rise in serum AAT (to < 6 microM). After treatment with antibiotics, in patients with AAT deficiency, there were significant changes in many sputum proteins including a rise in SLPI levels, and a reduction in myeloperoxidase (MPO) and elastase activity (p < 0. 005 for all measures); the sputum chemoattractants interleukin-8 (IL-8) and leukotriene B(4) (LTB(4)) fell (p < 0.01), and protein leak (sputum/serum albumin ratio) became lower (p < 0.01). The changes were rapid and within 3 d of the commencement of antibiotic therapy the biochemical markers had decreased significantly, but took a variable time thereafter to return to baseline values. In conclusion, patients with AAT deficiency had evidence of increased elastase activity at the start of the exacerbation when compared with nondeficient COPD patients which probably reflects a deficient antiproteinase screen (lower sputum AAT and SLPI). The increased bronchial inflammation at presentation resolved rapidly with 14 d of antibiotic therapy.