### 850 volume 122 | number 8 | August 2014 • Environmental Health Perspectives All EHP content is accessible to individuals with disabilities. A fully accessible (Section 508–compliant)
HTML version of this article is available at http://dx.doi.org/10.1289/ehp.1307240

.



### Introduction Nitrogen dioxide (NO 2 

### ), a ubiquitous atmospheric pollutant, is a respiratory irri

tant that remains a matter of concern [World Health Organization (WHO) European Centre for Environment and Health and WHO Regional Office for Europe 2013]. Indoor concentrations of NO 2 

### often exceed those found outdoors, especially when unvented combustion appliances are used. Inside homes, peak levels of NO 2 

### , associ

ated with the use of gas and solid-fuel appli

ances for cooking and heating, have been measured in the range of 80–1,100 ppb (150–2,090 μg/m 3 

### ) (Basu and Samet 1999; Dennekamp et al. 2001; Kotzias et al. 2005; Pilotto et al. 1997). Outdoors, hourly NO 2 

### concentrations in cities rarely exceed 200 ppb (380 μg/m 3 

### ) (U.S. Environmental Protection Agency 2008), although urban levels can reach levels as high as 500 ppb (950 μg/m 3 

### ) (WHO 2006), especially for short periods in streets with heavy traffic and in road tunnels (Larsson et al. 2010). Epidemiological and controlled human exposure studies suggest that people with asthma are more susceptible to the effects of NO 2 

### when compared with healthy individuals (Bauer et al. 1986; Belanger et al. 2006; Bylin

et al. 1988; Hasselblad et al. 1992; Jorres and Magnussen 1990; Strand et al. 1996). However, despite the extensive literature on NO 2 

### -induced health effects, some incon

sistencies in the results of studies have been noted (Jarvis et al. 2010). In asthmatics, NO 2 

### exposure without allergen challenge did not result in lung functional changes in most stud

ies (Avol et al. 1988; Kleinman et al. 1983;
Linn et al. 1986; Mohsenin 1987), and incon

sistent results were found in airway respon

siveness after nonspecific bronchoconstrictor challenges (Bylin et al. 1988; Hazucha et al. 1983; Jorres and Magnussen 1991; Kleinman

et al. 1983; Roger et al. 1990; Strand et al. 1996). After allergen challenge, exposure to NO 2 

### in asthmatics increased airway hyper

responsiveness (Jenkins et al. 1999; Strand

et al. 1997, 1998; Tunnicliffe et al. 1994) and eosinophilic inflammation (Barck et al. 2002, 2005). A few studies have investigated the inflammatory response to a single expo

sure of NO 2 

### without allergen challenge in asthmatics, but the findings have been inconsistent (Jorres et al. 1995; Solomon

et al. 2004; Vagaggini et al. 1996). We investigated whether repeated brief exposures to 200 ppb (380 μg/m 3 

### ) and 600 ppb (1,130 μg/m 3 

### ) NO 2 

### , which mimic indoor NO 2 

### peaks, enhance airway inflam

mation in asthmatics. This clinical study involved 19 adults with intermittent asthma and used a randomized double-blind protocol with assessment of inflammatory response in induced sputum.



### Materials and Methods
Participants . Nineteen patients [14 men and 5 women; median age, 29 years; age range, 20–69 years; median body mass index (BMI), 26 kg/m 2 

### ; BMI range, 20–39 kg/m 2 

### ] were included in the study (Table 1). All had intermittent asthma as defined by the Global Initiative for Asthma (2010) guidelines and were nonsmokers (18 had never smoked and 1 had stopped smoking some 10 years earlier).

Address correspondence to V. Ezratty, Service des Etudes Médicales (SEM), EDF–DRH GROUPE, 45 rue Kleber, Site Carré Vert, 92300 Levallois– Perret, France. Telephone: 00 33 (1) 82 24 84 43. E-mail: veronique.ezratty@edf.fr

Supplemental Material is available online (http:// dx.doi.org/10.1289/ehp.1307240).

We thank the following for their contributions:
I. Poirier, H. Casterman, S. Billot-Bonef, M. BonnetBelfais, E. Pigeon, S. Maestri, B. Vandercasteele,
L. Alavoine, L. Nardelli, A. Boulmeau, L. Dejoie, Y. Retory, S. de Ferrières, and D. Ormandy. All statis

tical analyses were performed by S. Koscielny, Service de biostatistiques et épidémiologie, Gustave Roussy, Villejuif, France.

This study was supported by the Center for Research & Innovation in Gas and New Energy Sources, CRIGEN, GDF SUEZ; the Medical Studies Department of EDF; and the Clinical Center of Investigation at Bichat Hospital, Paris, France.

The authors’ freedom to design, conduct, interpret and submit for publication the research described in this work was not compromised by any of the funding bodies.

V.E., G.G., P.-A.C., and J.L. are employed byEDF, Service des Etudes Médicales (SEM), LevalloisPerret, France. P.M., L.R., and S.T. are employed by GDF-SUEZ, Center for Research & Innovation in Gas and New Energy Sources CRIGEN, St-Denis, France. The other authors declare they have no actual or potential competing financial interests.

Received: 18 June 2013; Accepted: 15 April 2014; Advance Publication: 18 April 2014; Final Publication: 1 August 2014. 

# Repeated Nitrogen Dioxide Exposures and Eosinophilic Airway Inflammation in Asthmatics: A Randomized Crossover Study

Véronique Ezratty, 1 

### Gaëlle Guillossou, 1 

### Catherine Neukirch, 2 

### Monique Dehoux, 3 

### Serge Koscielny, 4 

### Marcel Bonay, 5 

### Pierre-André Cabanes, 1 

### Jonathan M. Samet, 6 

### Patrick Mure, 7 

### Luc Ropert, 7 

### Sandra Tokarek, 7 

### Jacques Lambrozo, 1 

### and Michel Aubier 2

1 Service des Etudes Médicales (SEM), EDF, Levallois-Perret, France; 2 Service de Pneumologie A, Clinical Center of Investigation, Inserm U700, Bichat Hospital, Université Paris Diderot, DHU FIRE, Paris, France; 3 Laboratoire de Biochimie, Bichat Hospital, Paris, France; 4 Service de biostatistiques et épidémiologie, Gustave Roussy, Villejuif, France; 5 Department of Physiology, Bichat Hospital, Paris, France; 6 Department of Preventive Medicine, Keck School of Medicine of the University of Southern California, Los Angeles, Los Angeles, California, USA; 7 Center for Research & Innovation in Gas and New Energy Sources, CRIGEN, GDF SUEZ, St-Denis, France

B ackground : Nitrogen dioxide (NO 2 ), a ubiquitous atmospheric pollutant, may enhance the asthmatic response to allergens through eosinophilic activation in the airways. However, the effect of NO 2 on inflammation without allergen exposure is poorly studied.

O b jectives : We investigated whether repeated peaks of NO 2 , at various realistic concentrations, induce changes in airway inflammation in asthmatics.

M ethods : Nineteen nonsmokers with asthma were exposed at rest in a double-blind, crossover study, in randomized order, to 200 ppb NO 2 , 600 ppb NO 2 , or clean air once for 30 min on day 1 and twice for 30 min on day 2. The three series of exposures were separated by 2 weeks. The inflammatory response in sputum was measured 6 hr (day 1), 32 hr (day 2), and 48 hr (day 3) after the first exposure, and compared with baseline values measured twice 10–30 days before the first exposure.

R esults : Compared with baseline measurements, the percentage of eosinophils in sputum increased by 57% after exposure to 600 ppb NO 2 ( p = 0.003) but did not change significantly after exposure to 200 ppb. The slope of the association between the percentage of eosinophils and NO 2 exposure level was significant ( p = 0.04). Eosinophil cationic protein in sputum was highly corre

lated with eosinophil count and increased significantly after exposure to 600 ppb NO 2 ( p = 0.001). Lung function, which was assessed daily, was not affected by NO 2 exposure.
C onclusions : We observed that repeated peak exposures of NO 2 performed without allergen expo

sure were associated with airway eosinophilic inflammation in asthmatics in a dose-related manner.

C itation : Ezratty V, Guillossou G, Neukirch C, Dehoux M, Koscielny S, Bonay M, Cabanes PA, Samet JM, Mure P, Ropert L, Tokarek S, Lambrozo J, Aubier M. 2014. Repeated nitrogen dioxide exposures and eosinophilic airway inflammation in asthmatics: a randomized crossover study. Environ Health Perspect 122:850–855; http://dx.doi.org/10.1289/ehp.1307240Environmental Health Perspectives
• volume 122 | number 8 | August 2014 

### 851 Only patients who had a diagnosis of asthma confirmed by a positive methacholine chal

lenge performed twice at baseline 10–30 days before the first exposure were included in the study. A positive methacholine test was defined as a methacholine provocative dose causing a 20% decrease in forced expiratory volume in 1 sec (FEV 1 

### ) from control FEV 1 

### (PD 20 

### methacholine) < 4 mg. All partici

pants had allergy to house dust mites (HDM)and/or pollen confirmed by a positive skinprick test done ≥ 4 weeks before their inclu

sion in the study. The study was performed outside the pollen season for those who had been diagnosed with pollen allergies. Of the 19 participants, 6 had a personal history of atopic dermatitis and/or an atopic familial history. None of those six used inhaled or oral corticosteroids or other anti inflammatory therapy, and the only permitted medication was an inhaled β 2 

### -agonist, used as needed during the study period (from baseline, i.e.,
30 days before the first NO 2 

### exposure until the end of the study 2 weeks after the last exposure). Participants who had gas stoves and/or unvented combustion appliances at home were told not to use them at baseline and on the days of exposures and during the
2 days before and after NO 2 

### exposure. All par

ticipants had to be free of airway infection for at least 6 weeks before baseline measurements. The study was registered by the French Ministry of Health (DGS 2006/0016) andapproved by the Ethics Committee of HotelDieu Hospital, Paris, France (project 0611398, registered on 28 February 2007). All partici

pants signed informed consent forms before enrollment in the study. Study design . The study had a doubleblind, crossover design, with each participant acting as his or her own control. For each par

ticipant, the study involved three series each of three exposures at rest: one series to clean air,
one series to 200 ppb (380 μg/m 3 

### ) NO 2 

### , and one series to 600 ppb (1,130 μg/m 3 

### ) NO 2 

### . The order of the three series of exposures was randomized (Figure 1). The design for each series of exposures with the timing of pulmo

nary function testing, and sputum inductions from day 1 to day 3 is described in Figure 2. For each series, participants were exposed to the same level of NO 2 

### or to clean air once for
30 min on day 1, and twice for 30 min on day 2, at the same time and on the same days of the week. The two exposures performed on day 2 were separated by 1 hr. There was no exposure on day 3. There was an interval of 2 weeks between each series of exposures. Only the engineer in charge of injection into the chamber knew whether the participant was being exposed to NO 2 

### or clean air. Sputum was induced twice at base

line (10–30 days before first exposure, with
1–3 weeks between the sputum inductions) and for each series of exposures, 6 hr (on day 1),
32 hr (on day 2), and 48 hr (on day 3) after the end of the first exposure. Spirometry with flow–volume curves was carried out at baseline (immediately before first exposure) and daily from day 1 to day 3, before and immediately after exposures, and immediately before spu

tum inductions. Allergen challenge was not performed, either before or after the exposures. Nitrogen dioxide/clean air exposure . The exposures were performed in an 8.8-m 3 

### expo

sure chamber installed in the investigation clinical center at the Hospital Bichat in Paris as previously described (Ezratty et al. 2007).The chamber was supplied with fresh, particlefree air at a mean temperature of 25°C and a mean relative humidity of 32%. The air supply passed through HEPA and activated carbon filters. We used NO 2 

### concentrated at 950 ppm compressed in a 20-L gas bottle under 150 bar pressure for the 600

- ppb expo

sures, and a gas bottle of NO 2 

### concentrated at 520 ppm under 150 bar pressure for the
200

- ppb exposures (Air Liquide SA, Paris, France). A mass flow meter secured the stabil

ity of the injected flow at the expected concen

tration (200 ppb or 600 ppb). During exposures, NO 2 

### concentration inside the exposure chamber was continu

ously monitored (chemiluminescence oxides of nitrogen analyzer, Model AC 32 M; Environnement SA, 78300 Poissy, France). The mean concentration was 581 ppb ± 3.2% for 600-ppb NO 2 

### exposures and 203 ppb

± 1.5% for 200-ppb NO 2 

### exposures. During exposures to clean air, the NO 2 

### concentration

was < 10 ppb. Pulmonary function and methacholine challenge testing . Flow-volume curves were obtained using a Biomedin spirometer (Biomedin srl, Padova, Italy) according to the European Community Respiratory Health Survey specifications to determine FEV 1 

### and peak expiratory flow (PEF) (Quanjer 1993). Methacholine challenge tests were donetwice at baseline with an automatic inhalationsynchronized Mefar MB3 dosime ter jet nebu

lizer (Mefar spa, Bovezzo, Italy), as described elsewhere (Aubier et al. 1992; Ezratty et al. 2007). Methacholine challenge tests at base

line were conducted 10–30 days before the start of the exposures to avoid any putative interference of the methacholine challenge with the effect of NO 2 

### (Jorres et al. 1995). Sputum induction and inflammatory marker measurements. We performed sputum

**Table 1.** Characteristics of participants.

Participant Age (years) History of atopy a Smoking

status Sex Height (cm) Weight (kg) BMI (kg/m 2 ) Asthma duration (years) FEV 1 at inclusion (FEV 1 % predicted) PD20 methacholine at baseline (μg) Percent eosinophils in sputum at baseline b

1 c 26 Yes N F 164 57 21 8 3.23 (110) 1,600 NA 2 29 No E M 185 90 27 11 4.13 (89) 1,490 14.73 3 29 No N M 182 87 27 10 4.43 (99) 690 11.88
4 31 No N M 161 84 33 8 2.87 (81) 3,200 6.79 5 28 No N M 174 74 25 4 3.69 (88) 1,550 1.68 6 27 No N M 180 88 28 21 3.57 (80) 1,220 0.93
7 24 No N M 178 70 22 8 3.88 (87) 1,070 4.25 8 30 No N F 159 56 22 20 3.03 (103) 500 2.68 9 29 Yes N M 168 72 26 22 3.89 (100) 3,200 1.88 10 c 28 Yes N M 186 92 27 2 4.49 (96) 800 ANR
11 20 Yes N F 158 49 20 9 2.29 (76) 930 0.26 12 69 No N M 178 90 29 5 2.49 (78) 3,200 17.72 13 30 No N F 163 55 21 20 2.68 (87) 1,950 32.08
14 32 Yes N M 179 82 26 24 4.12 (92) 340 2.51 15 24 No N F 171 60 21 14 3.41 (97) 310 5.12 16 28 No N M 174 62 21 16 3.82 (91) 2,100 20.58
17 32 No N M 176 115 38 21 4.16 (100) 2,170 2.99 18 c 30 Yes N M 169 89 32 21 3.75 (95) 190 NA 19 30 No N M 174 115 39 23 3.16 (76) 210 1.55

Abbreviations: ANR: available but not relevant because participant 10 did not complete the three series of exposure; E, ex-smoker; N, never-smoker; NA: not available.

a Personal history of atopic dermatitis and/or atopic familial history. b Percent eosinophils at baseline (10–30 days before first exposure). c Participants excluded from the analysis: par

ticipants 1 and 18 did not produce adequate sputum specimens for cell analysis at baseline (squamous cells > 20%); participant 10 did not complete the three series of exposure.

### 852 volume 122 | number 8 | August 2014 • Environmental Health Perspectives 

### induction with an aerosol of hypertonic saline using the method of Pin et al. (1992). The sputum was analyzed within 1 hr according to Pizzichini et al. (1996), as described elsewhere (Ezratty et al. 2007). Total non squamous inflammatory cell counts were expressed as
10 3 

### cells/mg of induced sputum. Differential cell counts were performed by counting 400 cells on May Grünwald Giemsa stained slides by two expert observers blinded to the participant’s exposure. Results were expressed both as percentage and as number of inflam

matory cells per milligram of induced sputum. Only samples with cell viability > 70% and squamous cell contamination < 20% were considered adequate. Sputum supernatant concentrations of eosinophil cationic protein (ECP) levels were measured by a commercially available enzyme assay (CAP-FEIA; Pharmacia, St Quentin-enYvelines, France), with a lower detection limit of 2 ng/mL. Follow-up during the study period . After 0, 15, and 30 min of exposure to NO 2 

### or clean air in the chamber, participants were asked questions relating to respiratory symptoms and perception of discomfort.
FEV 1 

### and PEF were monitored twice dur

ing exposure at 15-min intervals and hourly for 6 hr after leaving the chamber, with a por

table combined spirometer (One Flow Tester; Mediflux, Croissy Beaubourg, France). During the 10–30 days between baseline measurements and first exposure and during the 2-week interval following each series of exposures, subjective symptoms and medi

cations were recorded every day. Each par

ticipant measured FEV 1 

### and PEF twice daily with a portable combined spirometer. Sample size . The primary end point was the change in the percentage of eosinophils in sputum, expressed as the ratio between the percentage after exposure and the baseline percentage. When the study was designed, litera ture reports were insufficient to deter

mine the variance of the ratio, which was mandatory to estimate the sample size. Variance was estimated after inclusion of the first eight participants without unblind

ing. Based on the variance found of 0.10, a sample size of 18 participants was considered sufficient to demonstrate a doubling of the percentage of eosinophils in sputum with a power of 80% and a significance level of 0.05 (see Supplemental Material, Table S1). In addition, a doubling has been reported to be consistent with clinically relevant changes in clinical status of asthmatics (Green et al. 2002). Statistical analysis . The parameters studied in sputum were the percentage of eosino phils, the number of eosinophils per milligram, ECP, the number of neutrophils per milligram, and the number of macrophages per milligram. All parameters were log-transformed to normalize the distributions. We used a generalized linear model (GLM procedure, SAS v9.4; SAS Institute Inc., Cary, NC, USA) for the analy

ses. We included in the statistical model the effect of the participant, the time, the dose, and the interaction between the time and the dose. The interpretation of the results was based on the type III sum of squares. In case of a significant interaction between day and dose, a global analysis was performed, followed by per-day analyses. In the global analysis, all the data concerning the parameter were sum

marized by their geometric means (GMs) (in case of sputum inductions, this relates to three sputum inductions over 3 days, one per day), and we tested the relation between NO 2 

### concentration—used as a quantitative value (0, 200, and 600 ppb)—and the parameter studied. The global analysis provided the p trend



### . To display the results in a meaningful way, we also analyzed the data using classes of expo

sure (without any preconceived idea on the form of the relationship): For each class of exposure, we estimated the least-square mean (LSMEAN) and its 95% confidence limits. The LSMEANs and the confidence limits were exponentiated to obtain the changes relative to the baseline measurements and their con

fidence intervals (CIs). The per-day analyses were reported only when the trend in the global analysis was significant. p -Values < 0.05 were considered significant.



### Results Among the 19 participants, 18 completed the three series of exposures and were included in the analysis. Among those, two did not produce an adequate sample of sputum at all

**Figure 1.** Flow diagram of the study period for each participant. Abbreviations: H0, immediately before 1st exposure (day 1); H0’, immediately after 1st exposure (day 1); H6, 6 hr after H0’ (day 1); H32, 32 hr after H0’ (day 2); H48, 48 hr after H0’ (day 3). The dose order was attributed randomly; so, series A, B, and C corresponds to clean air, 200-ppb NO 2 , or 600-ppb NO 2 exposure. Sputum induction

Sputum induction Inclusion

Visit 1

Day 1

Day 2 1 exposure to dose A (30 min) from H0 to H0’

1 exposure to dose B (30 min) from H0 to H0’ 2 exposures to dose A (2 × 30 min) + H6 sputum induction

+ H6 sputum induction + H32 sputum induction

+ H32 sputum induction Series A dose A teste d

Series B dose B teste d

Series C dose C tested Visit 2

Day 3

Day 1

Day 2

Day 3 2 weeks wash out No exposure

2 exposures to dose B (2 × 30 min)

No exposure

1 exposure to dose C (30 min) from H0 to H0’

2 exposures to dose C (2 × 30 min)

No exposure + H48 sputum induction

+ H48 sputum induction

+ H6 sputum induction

+ H32 sputum induction

+ H48 sputum induction Day 1

Day 2

Day 3

2 weeks follow-up 2 weeks wash out 1–3 weeksBASELINEEnvironmental Health Perspectives
• volume 122 | number 8 | August 2014 

### 853 time points and were not included in analyses of sputum (Table 1). Respiratory function—FEV 1 

### and PEF— measured by spirometry, did not signifi

cantly change after NO 2 

### exposure compared with clean air exposure (Table 2). No major clinical adverse reactions, such as cough

ing, wheezing, or chest tightness suggesting asthma attacks, were observed during expo

sures or follow-up. During the 2 weeks after each exposure, subjective symptoms and peak flow measurements were not significantly different regardless of exposure. The primary analysis tested the expo

sure level (dose), the time (because the study design included assessment at three time points after exposure, one each day) and the interaction between time and exposure level. The dose was significantly related to the change in the percentage of eosino

phils, the time was not. There was a signifi

cant interaction between time and exposure level, meaning that the association between dose and effect on eosinophils was different according to the day. As planned in the case of a significant inter action, we performed both a global analysis, averaging the measure

ments over the 3 days, and per-day analyses. In the global analysis, the slope of the association between the percentage of eosino

phils and NO 2 

### exposure level was significant ( p = 0.04) (Table 3). Compared with baseline measurements, the percentage of eosinophils in sputum increased by 57% (95% CI: 18, 109%) after 600 ppb NO 2 

### ( p = 0.003) but did not change significantly after clean air or after
200 ppb NO 2 

### . Similar results were found for the associa

tion between the number of eosinophils per milligram of sputum and NO 2 

### exposure level. In the global analysis, the slope of the asso

ciation was significant ( p = 0.02) (Table 3). The number of eosinophils per milligram of sputum increased by 120% (95% CI: 60, 202%) after 600 ppb NO 2 

### ( p < 0.001) but not after clean air or after 200 ppb NO 2 

### (Table 3). Per-day analysis showed that the slope of the association between the percentage of eosinophils and NO 2 

### exposure level was not significant at day 1 ( p = 0.81), but was signifi

cant at day 2 ( p = 0.01) and day 3 ( p = 0.03). A similar pattern was found for the slope of the association between the number of eosino

phils per milligram of sputum and the level of exposure to NO 2 

### , which was not significant at day 1 ( p = 0.10), close to significance at day 2 ( p = 0.06), and significant at day 3 ( p = 0.03) (Table 3; see also Supplemental Material, Figure S1). Compared with baseline measurements, there was no significant change of the per

centage of eosinophils in sputum regardless of the level of exposure to NO 2 

### at day 1. At day 2, the percentage and the number of

**Figure 2.** Study design for each of the three series of exposures separated by 2 weeks. Abbreviations: H0, immediately before 1st exposure (day 1); H0’, immedi

ately after 1st exposure (day 1); H6, 6 hr after H0’ (day 1); H32, 32 hr after H0’ (day 2); H48, 48 hr after H0’ (day 3). Participants were exposed at rest in a doubleblinded, randomized, crossover design to clean air, 200-ppb NO 2 , or 600 ppb NO 2 once for 30 min on day 1, and twice for 30 min on day 2. There was no exposure on day 3. Time of day is expressed in military form. 0915 hours 30 min

**H48 H0**  **H0’ H6**  **× 2** 

**× 2** 

**H3 2**  **H2 6** 

30 min 30 min **H24**

< 1 hr > Day 2 Day 1

Day 3 **Arrive at hospital**  0800 hours

**Arrive at hospital**  0800 hours

Methacholine Bronchial challenge

• PD 20 methacholine **Arrive at hospital**  0800 hours **Leave hospital** around 1730 hours Baseline: 10–30 days before first exposure

**Leave hospital** around 1730 hours

**Leave hospital** around 1100 hours 0845 hours

0845 hours 1015 hours 1045 hours

0845 hours 0915 hours NO 2 /air

NO 2 /air NO 2 /air

Induced sputum Exposure to
• NO 2 200 ppb, or
• NO 2 600 ppb, or
• Clean air Spirometry

• Flow volume curv e Portable spirometry

• FE V 1 + PE F

### 854 volume 122 | number 8 | August 2014 • Environmental Health Perspectives 

### eosinophils increased significantly at 600 ppb, but not at 200 ppb NO 2 

### . At day 3, the num

ber of eosinophils increased significantly
at 200 ppb and at 600 ppb NO 2 

### , and the increase of the percentage of eosinophils was close to significance at 600 ppb NO 2 

### , but not significant at 200 ppb (Table 3; see also Supplemental Material, Figure S1). Absolute values not baseline adjusted [GMs (95% CIs)] of the percentages of
eosino phils are reported in Supplemental Material, Table S2. Individual plots of the percentage of eosinophils are displayed in Supplemental Material, Figure S2. In order to see if results were driven by a participant in particular, we did a sensitivity analysis: a series of analyses with one different partici

pant removed for each analysis. The trend test that measures the relationship between the dose of NO 2 

### and the increase of the percent

age of eosinophils in sputum from baseline was significant ( p < 0.05) in 10 of the tests, and was close to significance ( p

< 0.10) for the other participants. Moreover, the increase of the percentage of eosinophils in sputum com

pared with baseline measurements was always significant at 600 ppb, regardless of which partici pant was removed from the analysis (see Supplemental Material, Table S3). There was a significant correlation between the number of eosinophils per milligram of sputum and ECP (in nanograms per milliliter) ( p < 0.001) (see Supplemental Material, Figure S3). Compared with baseline measurements, ECP in sputum increased significantly after exposure to 600 ppb NO 2 

### (43%; 95% CI: 17, 75%; p = 0.001) but not after exposure to clean air or 200 ppb NO 2 

### . However, the slope of the association between ECP and the level of exposure was not significant (Table 3). Exposure to NO 2 

### did not affect the other cell types (macrophages, neutrophils) measured in sputum (Table 3). There was no correlation between methacholine challenge tests and eosinophil responses (data not shown).



### Discussion Our findings indicate that repeated brief exposures to NO 2 

### without allergen exposure increase eosinophilic airway inflammation in participants with intermittent asthma with

out inducing any changes in lung function. Because only mild asthmatics were tested, the results cannot be extrapolated to healthy individuals. Although we cannot exclude that repeated challenges with hypertonic saline could have potentialized the effect of NO 2 

### , the repeti

tion of sputum inductions is not the cause of the effect because the effect is expected to be the same for each of the three series of expo

sures (Pavord 1998). Eosinophils in sputum increased according to NO 2 

### exposure level,and this significant trend supports a doserelated relationship. The effect on eosinophils and on ECP in sputum was significant at 600 ppb NO 2 

### . We found a strong correlation between ECP and eosinophils, suggesting that eosinophils were activated. In participants with asthma, several studies have found that NO 2 

### exposure increased eosinophilic inflammation in response to inhaled allergen, in the distal lower airways assessed by bronchial wash and broncho

alveolar lavage (BAL) (Barck et al. 2002), and in sputum (Barck et al. 2005). The three previous studies that have investigated effects of NO 2 

### without allergen challenge in partici

pants with asthma did not find changes in inflammatory cell distributions in BAL (Jorres

et al. 1995) and in sputum (Solomon et al. 2004; Vagaggini et al. 1996). However, these studies involved small numbers of participants, and no repetition of exposure, and, in the study by Jorres et al. (1995), the evaluation of inflammation could have been performed too soon after exposure. In the present study, participants with asthma were exposed to two realistic NO 2 

### concentrations: 200 ppb and 600 ppb of NO 2 

### , which are close to NO 2 

### peaks likely to be found indoors during the use of com

bustion appliances for cooking and heating (Basu and Samet 1999; Dennekamp et al. 2001; Kotzias et al. 2005; Pilotto et al. 1997) and outdoors for short periods in streets with heavy traffic and in road tunnels (Larsson

et al. 2010). Exposures lasted 30 min, close to the average time spent cooking dinner in France (38 min during the week and 46 min the weekend in a 2003 survey) (Hébel 2012). Furthermore, exposure to intermit

tent peaks of NO 2 

### may have greater effects than long-term, low-level exposure (Gardner

et al. 1979). Exposures in the present study were repeated over 2 days to mimic how exposures take place in real life and in order to assess a possible cumulative effect. At day 1, after one exposure, there was no significant change in eosinophilic airway inflammation—contrary to day 2 and day 3, after three exposures. These findings suggest that inflammatory response to NO 2 

### exposure may be delayed or that a single exposure may be insufficient to enhance eosinophilic airway inflammation, suggesting a cumulative effect of NO 2 

### . These results are consistent with those of Barck et al. (2005) who found that two to three brief exposures at 260 ppb NO 2 

### were needed to promote an increase in the airway inflamma

tory response to inhaled allergens. In addition to the study by Barck et al. (2005), our study shows that NO 2 

### , without an exposure to a high concentration of allergens, as with an allergen challenge, is sufficient to enhance inflammation in the airways. This finding could be of significance because exposure to peaks of NO 2 

### is common, particularly indoors, whereas exposure to both high con

centrations of NO 2 

### and the specific stimu

lus for a susceptible individual is less likely (Hesterberg et al. 2009). Many cities in Europe show an increase in concentrations of NO 2 

### measured close to traffic due to the increasing number of vehicles, in particular diesel vehicles. Exhaust emissions from diesel vehicles are lower for carbon monoxide, non-methanic volatile organic compounds, and particulate matter **Table 2.** GM s (95% CI s ) of values relative to baseline of FEV 1 and PEF evaluated in the 18 participants who completed the study.

Variable 0 ppb NO 2 (clean air) 200 ppb NO 2 600 ppb NO 2 p -Value

FEV 1 /baseline 1.02 (1.00, 1.05) 1.00 (0.97, 1.03) 1.00 (0.98, 1.03) 0.41 PEF/baseline 1.05 (0.99, 1.11) 1.04 (0.98, 1.10) 1.01 (0.96, 1.07) 0.36
Baseline values were measured immediately before first exposure (H0 on day 1) for each series of exposure. Each value corresponds to the GM change from baseline of the six values [H0’, immediately after first exposure (day 1); H6, 6 hr after H0’ (day 1); H32, 32 hr after H0’ (day 2); H48, 48 hr after H0’ (day 3)] obtained by spirometry with flow-volume curves. The effects of exposure, regardless of the dose, on FEV 1 and PEF were not significant.

**Table 3.** Changes relative to baseline measurements (performed 10–30 days before the first exposure) for parameters measured in sputum [GM % (95% CI), n = 16].

Variable 0 ppb NO 2 (clean air) 200 ppb NO 2 600 ppb NO 2 p Trend Percentage of eosinophils –12 (–34, 16) –5 (–28, 26) 57 (18, 109)** 0.04

Day 1 16 (–28, 86) –34 (–59, 6) 12 (–31, 79) 0.81 Day 2 –5 (–37, 44) –3 (–36, 46) 102 (32, 211)** 0.01 Day 3 –39 (–67, 13) 36 (–26, 149) 79 (–3, 230) 0.03 No. of eosinophils/mg –5 (–31, 29) 23 (–10, 68) 120 (60, 202) # 0.02 Day 1 –5 (–44, 60) –24 (–55, 29) 64 (–3, 177) 0.10 Day 2 9 (–39, 95) 23 (–31, 119) 142 (32, 344)** 0.06 Day 3 –18 (–57, 56) 99 (5, 278)* 163 (38, 398)** 0.03 ECP 21 (–1, 47) 0 (–18, 22) 43 (17, 75)** 0.23 No. of neutrophils/mg 12 (–17, 51) –9 (–32, 22) 10 (–19, 49) 0.97 No. of macrophages/mg –18 (–33, 0) –2 (–20, 21) –6 (–24, 15) 0.46
GM percentages represent all changes of the parameter for the 3 days (one sputum induction per day).

* p

< 0.05; ** p < 0.01; and # p < 0.001, compared with baseline.Environmental Health Perspectives
• volume 122 | number 8 | August 2014 

### 855 but may be higher for NO 2 

### (Guerreiro et al. 2012). Although epidemiological studies on NO 2 

### have several limitations in particular because of the potential for exposure mis

classification and co-pollutant effects, our results provide important evidence suggesting that NO 2 

### alone has a direct effect on airway inflammation in asthmatics.



### Conclusions To our knowledge, this is the first study to demonstrate that repeated peaks of NO 2 

### at realistic concentrations without allergen expo

sure increase eosinophilic inflammation in the airways of asthmatics, supporting a dose– response relationship. Although it is difficult to evaluate the clinical implications of these findings in the present study, an increased eosinophilic inflammation may lead to exac

erbation or loss of control of asthma (Green

et al. 2002; Jacobsen et al. 2007). Therefore, we cannot rule out the effects of repeated exposures to NO 2 

### over a longer period of time or effects in subpopulations.

**R efe**  **r ences** 

Aubier M, Levy J, Clerici C, Neukirch F, Herman D. 1992. Different effects of nasal and bronchial glucocortico

steroid administration on bronchial hyperresponsive

ness in patients with allergic rhinitis. Am Rev Respir Dis 146(1):122–126. Avol EL, Linn WS, Peng RC, Valencia G, Little D, Hackney JD. 1988. Laboratory study of asthmatic volunteers exposed to nitrogen dioxide and to ambient air pollution. Am Ind Hyg Assoc J 49(4):143–149. Barck C, Lundahl J, Halldén G, Bylin G. 2005. Brief exposures to NO2 augment the allergic inflammation in asthmatics. Environ Res 97(1):58–66. Barck C, Sandstrom T, Lundahl J, Hallden G, Svartengren M, Strand V, et al. 2002. Ambient level of NO 2 augments the inflammatory response to inhaled allergen in asthmatics. Respir Med 96(11):907–917. Basu R, Samet J. 1999. A review of the epidemiological evidence on health effects on nitrogen dioxide from gas stove. J Environ Med 1(4):173–187. Bauer MA, Utell MJ, Morrow PE, Speers DM, Gibb FR. 1986. Inhalation of 0.30  ppm nitrogen dioxide potentiates exercise-induced bronchospasm in asthmatics. Am Rev Respir Dis 134(6):1203–1208. Belanger K, Gent JF, Triche EW, Bracken MB, Leaderer BP. 2006. Association of indoor nitrogen dioxide exposure with respiratory symptoms in children with asthma. Am J Respir Crit Care Med 173(3):297–303. Bylin G, Hedenstierna G, Lindvall T, Sundin B. 1988. Ambient nitrogen dioxide concentrations increase bronchial responsiveness in subjects with mild asthma. Eur Respir J 1(7):606–612. Dennekamp M, Howarth S, Dick CA, Cherrie JW, Donaldson K, Seaton A. 2001. Ultrafine particles and nitrogen oxides generated by gas and electric cooking. Occup Environ Med 58(8):511–516. Ezratty V, Bonay M, Neukirch C, Orset-Guillossou G, Dehoux M, Koscielny S, et  al. 2007. Effect of formaldehyde on asthmatic response to inhaled allergen challenge. Environ Health Perspect 115:210–214; doi:10.1289/ehp.9414. Gardner DE, Miller FJ, Blommer EJ, Coffin DL. 1979. Influence of exposure mode on the toxicity of NO 2 . Environ Health Perspect 30:23–29. Global Initiative for Asthma. 2010. Global Strategy for Asthma Management and Prevention. Global Initiative for Asthma (GINA) 2010. Available http://www.ginasthma.org/local/ uploads/files/GINA_Report_2010_1.pdf. [accessed 9 July 2014]. Green RH, Brightling CE, McKenna S, Hargadon B, Parker D, Bradding P, et al. 2002. Asthma exacerbations and sputum eosinophil counts: a randomised controlled trial. Lancet 360(9347):1715–1721. Guerreiro C, de Leeuw F, Foltescu V, Schilling J, van Aardenne J, Lükewille A, et al. 2012. Air Quality in Europe — 2012 Report. Copenhagen:European Environment Agency. Available: http://www.eea.europa.eu/publications/ air-quality-in-europe-2012/at_download/file. [accessed 13 March 2014]. Hasselblad V, Eddy D, Kotchmar D. 1992. Synthesis of environ

mental evidence: nitrogen dioxide epidemiology studies. J Air Waste Manag Assoc 42(5):662–671. Hazucha MJ, Ginsberg JF, McDonnell WF, Haak ED Jr, Pimmel RL, Salaam SA, et al. 1983. Effects of 0.1 ppm nitro

gen dioxide on airways of normal and asthmatic subjects. J Appl Physiol 54(3):730–739. Hébel P. 2012. Comportements et consommations alimentaires
en France. Paris:Lavoisier. Hesterberg TW, Bunn WB, McClellan RO, Hamade AK, Long CM, Valberg PA. 2009. Critical review of the human data on short-term nitrogen dioxide (NO 2 ) exposures: evidence for NO 2 no-effect levels. Crit Rev Toxicol 39(9):743–781. Jacobsen EA, Ochkur SI, Lee NA, Lee JJ. 2007. Eosinophils and asthma. Curr Allergy Asthma Rep 7(1):18–26. Jarvis DJ, Adamkiewicz G, Heroux ME, Rapp R, Kelly FJ. 2010. Nitrogen dioxide. In: WHO Guidelines for Indoor Air Quality: Selected Pollutants. Copenhagen:World Health Organization, Regional Office for Europe. Available: http:// www.euro.who.int/__data/assets/pdf_file/0009/128169/ e94535.pdf [accessed 13 March 2014]. Jenkins HS, Devalia JL, Mister RL, Bevan AM, Rusznak C, Davies RJ. 1999. The effect of exposure to ozone and nitro

gen dioxide on the airway response of atopic asthmatics to inhaled allergen: dose- and time-dependent effects. Am J Respir Crit Care Med 160(1):33–39. Jorres R, Magnussen H. 1990. Airways response of asthmatics after a 30 min exposure, at resting ventilation, to 0.25 ppm NO 2 or 0.5 ppm SO 2 . Eur Respir J 3(2):132–137. Jorres R, Magnussen H. 1991. Effect of 0.25 ppm nitrogen dioxide on the airway response to methacholine in asymptomatic asthmatic patients. Lung 169(2):77–85. Jorres R, Nowak D, Grimminger F, Seeger W, Oldigs M, Magnussen H. 1995. The effect of 1 ppm nitrogen dioxide on  bronchoalveolar lavage cells and inflammatory mediators in normal and asthmatic subjects. Eur Respir J 8(3):416–424. Kleinman MT, Bailey RM, Linn WS, Anderson KR, Whynot JD, Shamoo DA, et al. 1983. Effects of 0.2 ppm nitrogen diox

ide on pulmonary function and response to broncho

provocation in asthmatics. J Toxicol Environ Health 12(4–6):815–826. Kotzias D, Koistinen K, Kephalopoulos S, Schlitt C, Carrer P, Maroni M, et  al. 2005. The INDEX Project. Critical Appraisal of the Setting and Implementation of Indoor Exposure Limits in the EU. Luxenbourg:Office for Official Publication of the European Communities. Available: http://ihcp.jrc.ec.europa.eu/our_activities/public-health/ index_final_report/at_multi_download/file?name=1622%20 -%20INDEX%20%20EUR%2021590%20EN%20report[1].pdf [accessed 13 March 2014]. Larsson BM, Grunewald J, Skold CM, Lundin A, Sandstrom T, Eklund A, et  al. 2010. Limited airway effects in mild asthmatics after exposure to air pollution in a road tunnel. Respir Med 104(12):1912–1918. Linn W, Shamoo D, Avol E, Whynot JD, Anderson KR, Venet TG, et al. 1986. Dose-response study of asthmatic volunteers exposed to nitrogen dioxide during intermittent exercise. Arch Environ Health 41(5):292–296. Mohsenin V. 1987. Airway responses to nitrogen dioxide in asthmatic subjects. J Toxicol Environ Health 22(4):371–380. Pavord ID. 1998. Sputum induction to assess airway inflamma

tion: is it an inflammatory stimulus? Thorax 53(2):79–80. Pilotto L, Douglas R, Attewell R, Wilson S. 1997. Respiratory effects associated with indoor nitrogen dioxide exposure in children. Int J Epidemiol 26(4):788–796. Pin I, Gibson PG, Kolendowicz R, Girgis-Gabardo A, Denburg JA, Hargreave FE, et  al. 1992. Use of induced sputum cell counts to investigate airway inflammation in asthma. Thorax 47(1):25–29. Pizzichini E, Pizzichini MM, Efthimiadis A, Evans S, Morris MM, Squillace D, et al. 1996. Indices of airway inflammation in induced sputum: reproducibility and validity of cell and fluid-phase measurements. Am J Respir Crit Care Med 154(2 Pt 1):308–317. Quanjer PH (ed). 1983. Standardized lung function testing. Bull Eur Physiopathol Respir 19(suppl 5):45–51. Roger LJ, Horstman DH, McDonnell W, Kehrl H, Ives PJ, Seal E, et al. 1990. Pulmonary function, airway responsive

ness, and respiratory symptoms in asthmatics following exercise in NO 2 . Toxicol Ind Health 6(1):155–171. Solomon C, Balmes JR, Kleinman M. 2004. Effects of Nitrogen Dioxide on Airway Inflammation in Allergic Asthmatic Subjects. Contract number 00-337. San Francisco:California Air Resources Board, California Environmental Protection Agency. Available: http://www.arb.ca.gov/research/apr/ past/00-337.pdf [accessed 13 March 2014]. Strand V, Rak S, Svartengren M, Bylin G. 1997. Nitrogen dioxide exposure enhances asthmatic reaction to inhaled aller

gen in subjects with asthma. Am J Respir Crit Care Med 155(3):881–887. Strand V, Salomonsson P, Lundahl J, Bylin G. 1996. Immediate and delayed effects of nitrogen dioxide exposure at an ambient level on bronchial responsiveness to histamine in subjects with asthma. Eur Respir J 9(4):733–740. Strand V, Svartengren M, Rak S, Barck C, Bylin G. 1998. Repeated exposure to an ambient level of NO 2 enhances asthmatic response to a nonsymptomatic allergen dose. Eur Respir J 12(1):6–12. Tunnicliffe WS, Burge PS, Ayres JG. 1994. Effect of domestic concentrations of nitrogen dioxide on airway responses to inhaled allergen in asthmatic patients. Lancet 344(8939–8940):1733–1736. U.S. Environmental Protection Agency. 2008. Integrated Science Assessment for Oxides of Nitrogen—Health Criteria (Final Report). Washington, DC:U.S. EPA. Available: http:// cfpub.epa.gov/ncea/cfm/recordisplay.cfm?deid=194645 [accessed 13 March 2014]. Vagaggini B, Paggiaro PL, Giannini D, Franco AD, Cianchetti S, Carnevali S, et al. 1996. Effect of short-term NO 2 exposure on induced sputum in normal, asthmatic and COPD sub

jects. Eur Respir J 9(9):1852–1857. WHO (World Health Organization). 2006. Air Quality Guidelines. Global Update 2005. Copenhagen:WHO Regional Office for Europe. Available: http://www.euro.who.int/__data/assets/ pdf_file/0005/78638/E90038.pdf [accessed 13 March 2014]. WHO (World Health Organization) European Centre for Environment and Health, WHO Regional Office for Europe. 2013. Review of Evidence on Health Aspects of Air Pollution—REVIHAAP Project. First Results. Copenhagen:WHO Regional Office for Europe. Available: http://www.euro.who.int/__data/assets/pdf_file/0020/182432/ e96762-final.pdf [accessed 13 March 2014].