Volume 112, Issue 2 , Pages 362-368, August 2003
Exposure and sensitization to indoor allergens: Association with lung function, bronchial reactivity, and exhaled nitric oxide measures in asthma☆
Article Outline
Abstract
Background: Exposure to high levels of allergens in sensitized asthmatic patients causes worsening of pulmonary function in experimental studies. Chronic exposure to lower, naturally occurring levels of allergens might increase the severity of asthma. Objective: We sought to study the associations between sensitization and exposure to common indoor allergens (dust mite, cat, and dog) in the home on pulmonary function, exhaled nitric oxide (eNO), and airway reactivity in asthmatic patients. Methods: Dust samples were collected from the living room carpet and mattress of 311 subject's homes, and Der p 1, Fel d 1, and Can f 1 concentrations were measured by using ELISAs. Spirometry, nonspecific bronchial reactivity, and eNO were measured. Results: Subjects both sensitized and exposed to high levels of sensitizing allergen had significantly lower FEV1 percent predicted values (mean, 83.7% vs 89.3%; mean difference, 5.6%; 95% CI, 0.6%-10.6%; P = .03), higher eNO values (geometric mean [GM], 12.8 vs 8.7 ppb; GM ratio, 0.7; 95% CI, 0.5-0.8; P = .001), and more severe airways reactivity (PD20 GM, 0.25 vs 0.73 mg; GM ratio, 2.9; 95% CI, 1.6-5.0; P < .001) compared with subjects not sensitized and exposed. No significant effect of the interaction between sensitization and exposure was found for FEV1 percent predicted and eNO values. However, there was a significant effect of the interaction between sensitization and exposure to any allergen (P = .05) and between sensitization and exposure to cat allergen (P = .04) for nonspecific bronchial reactivity. Conclusion: Asthmatic subjects who are exposed in their homes to allergens to which they are sensitized have a more severe form of the disease. (J Allergy Clin Immunol 2003;112:362-8.)
Keywords: Asthma severity and control, allergen exposure-sensitization, bronchial reactivity, lung function
Abbreviations: BR: , Bronchial reactivity, eNO: , Exhaled nitric oxide, GM: , Geometric mean, NS/E: , Not sensitized but exposed to any study allergens, NS/NE: , Not sensitized and not exposed to any study allergens, S/E: , Sensitized and exposed to 1 or more specific allergens, S/NE: , Sensitized but not exposed to any study allergens
Considerable data have accumulated regarding allergen exposure in relation to specific sensitization in children.1 The deleterious effect of sensitization to inhaled allergens on lung function and bronchial reactivity (BR) has been suggested,2, 3 but data on the importance of individual allergens have often been conflicting. In one survey, sensitization to dust mite, cat, and mold was a predictor of increased BR, whereas sensitization to outdoor allergens (timothy grass and birch) was not.2 Analysis of the Spanish data collected through the European Community Respiratory Health Study,4 however, showed that sensitization to timothy grass, Alternaria species, and cat allergen, but not mite allergen, was associated with a lower FEV1 after adjusting for bronchial hyperreactivity, respiratory symptoms, and smoking.
The underlying mechanism of asthma is airway inflammation,5 and chronic inflammation might lead to airway remodeling. Recent studies in animals have demonstrated structural remodeling changes occurring in the airways of rats that were sensitized and chronically exposed to allergens.6, 7 In human experimental studies allergen challenge causes early and late decreases in lung function.8 However, the concentration of allergen used in challenges is much greater than the exposure level in the domestic environment, albeit for a shorter period. The chronic exposure to allergens over long periods might contribute to the irreversible airway obstruction and severe BR seen in patients with chronic asthma. Very few studies have investigated the association of real-life allergen exposure and its interaction with sensitization on asthma control and severity in adults.
We aimed to examine the relationship between sensitization and exposure to indoor allergens in homes and their interaction and objective measures of asthma severity in a large group of asthmatic patients with a range of severity of disease.
Methods
Subjects provided written informed consent and were recruited into the study if they had a physician diagnosis of asthma with symptoms requiring treatment with at least a short-acting bronchodilator in the previous 12 months. Study participants were selected randomly from a clinical trial database of asthmatic patients. The subjects were from the Greater Manchester area, United Kingdom, and were a mixture of hospital and primary care patients.
The study protocol was approved by the local research ethics committee. Subjects attended the research unit having avoided short-acting bronchodilators (6 hours); long-acting bronchodilators, theophyllines, and leukotriene antagonists (12 hours); and antihis-tamines (48 hours). The following investigations were performed.
Pulmonary function testing
FEV1 and forced vital capacity were measured with a Microlab 3000 spirometer (MicroMedical, Rochester, United Kingdom). FEV1 percent predicted was calculated by using European Coal and Steel reference values.9
Assessment of airway reactivity
For subjects with an FEV1 of greater than 60% of the predicted value, a modified Yan technique bronchial challenge10 was used to obtain a cumulative PD20 FEV1 value. For technical and supply reasons, either histamine or methacholine was used for the provocation. The concentrations differed slightly (ie, histamine, 3.13 to 50 mg/mL; methacholine, 1.56 to 50 mg/mL). Previous studies11, 12 have shown that the 2 compounds produce similar results, and dose equivalence was presumed for our study.
A Koko DigiDoser dosimeter (PDS Research, Louisville, Colo) and “646” nebulizer pots (Devilbiss, Somerset, Pa) calibrated to deliver 10 μL per breath actuation during a tidal inspiration were used for the challenge. The PD20 FEV1 was calculated (by using cumulative doses) with the following formula: PD20 = Antilog[log D1 + (log D2 − log D1)(20 − R1]/(R2 − R1)].
The equation is derived from linear interpolation. In subjects who did not demonstrate a 20% decrease in FEV1 after the challenge, a PD20 of 12 mg was entered as the result (one doubling dose above the final cumulative dose).
Exhaled nitric oxide
Exhaled nitric oxide (eNO) was measured before spirometry and bronchial challenge with a chemiluminescence analyzer (LR 2000; Logan Research, Rochester, United Kingdom) with a resolution of 1 ppb, according to published guidelines.13 The response time (10%-90%) was less than 0.6 seconds, and the sampling rate was 250 mL/min. To measure eNO, subjects inhaled fully to total lung capacity and then immediately exhaled slowly (at a controlled rate of 6 L/min) to residual volume into a wide-bore Teflon tube with minimal resistance. The NO reading was taken when the level had reached a plateau and the CO2 concentration exceeded 5%. The mean of 2 readings was taken. The pressure during expiration was kept constant at 3 ± 0.4 mm Hg (by using a visual light display of expiratory flow), which was measured by using the pressure and volume sensors in the analyzer.
Skin prick testing
Sensitization was assessed by means of skin prick testing to common indoor allergens (Dermatophagoides pteronyssinus , cat, and dog; Bayer, Elkhart, Ind). The result was considered positive if the mean of 2 perpendicular diameters across the wheal was at least 3 mm greater than that produced by the negative control.
Home visits and assessment of allergen exposure
Dust samples were collected by vacuuming a 1-m2 area of the living room carpet and mattress. All samples were assayed for Der p 1, Fel d 1, and Can f 1 content by using ELISAs, as previously described.14, 15, 16 The results were expressed as micrograms of allergen per gram of fine dust, and the limit of detection was 0.05 μg/g for Der p 1, 0.08 μg/g for Fel d 1, and 0.2 μg/g for Can f 1.
Statistical analysis
Statistical analysis was performed with SPSS 10.0 for Windows (SPSS, Chicago, Ill). The conventional 5% level of statistical significance was used. A loge transformation of PD20 and eNO was required to produce an adequate approximation to a normal distri-bution, and geometric means (GMs) are presented as summary statistics. To test the hypothesis that the sensitized and exposed subgroup differs from the other 3 groups in the study, we performed an overall ANOVA together with a planned contrast of both sensitized and exposed patients versus patients from all other groups combined. This latter comparison does not necessarily prove that the sensitized and exposed group is significantly different from the 3 other subgroups, only that it is different from the average of the 3 other subgroups.
If the overall ANOVA result was found to be statistically significant, then individual comparisons between pairs of groups by using the Scheffe test were also reported.
The independent effects of sensitization and exposure were assessed by using an ANOVA model with main factors of sensitized versus not sensitized and exposed versus not exposed and the interaction of sensitized versus not sensitized × exposed versus not exposed together with the potential confounding factors (age, sex, family history of asthma, smoking history, and use of inhaled steroids). ANOVA was used because this is the conventional statistical approach to assess the effects of factors after adjusting for interactions and to evaluate the strength of the interaction between factors.
The following tests were performed to assess for the potential bias between the methacholine and histamine challenge:
Results
Three hundred eleven subjects were recruited into the study. Demographics and baseline results are listed in Table I.
Table I. Demographic details and baseline results
| Measure | Value |
|---|---|
| Age | 10-68 y (mean, 42 y; 95% CI, 41-44 y) |
| Sex | |
| Male | 128 (41.2%) |
| Female | 183 (58.8%) |
| Smoking status | |
| Smokers | 42 (13.5%) |
| Nonsmokers | 269 (86.5%) |
| Asthma treatment | |
| Receiving inhaled steroids | 197 (63%) (mean dose, 728 μg; median dose, 500 μg; 95% CI, 659-797 μg) |
| Not receiving inhaled steroids | 114 (37%) |
| FEV1 percent predicted | n = 311; range, 25%-131% (mean, 88%; 95% CI, 85%-90%) |
| PD20 | n = 179; range, 0.02-12.0 mg (GM, 0.44 mg; 95% CI, 0.34-0.57) |
| Exhaled nitric oxide | n = 265; range, 0.7-250 ppb (GM, 10.5 ppb; 95% CI, 9.4-11.7 ppb) |
| Atopic status (n = 311) | n = 306; not known, n = 5 |
| Atopic | 248 (80%) |
| Nonatopic | 58 (19%) |
| Allergen sensitization (positive test results) | |
| Dust mite | 186 (60%) |
| Cat | 151 (49%) |
| Dog | 125 (40%) |
Indoor allergen levels
Allergen levels for all subjects, as well as for pet owners, are listed in Table II.
Table II. Allergen level in homes visited
| GM (μg/g), range (95% CI) | |||
|---|---|---|---|
| Der p 1 | Can f 1 | Fel d 1 | |
| All subjects (n = 311) | |||
| Mattress | 1.60, 0.04-305 (1.19-2.10) | 0.74, 0.05-780 (0.56-0.97) | 1.24, 0.05-940 (0.90-1.71) |
| Living room | 1.72, 0.04-150.0 (1.33-2.23) | 2.78, 0.05-2150 (2.06-3.75) | 3.27, 0.05-1870 (0.38-4.46) |
| Pet owners (n = 135) | Dog owners (n = 58) | Cat owners (n = 81) | |
| Mattress | 2.03, 0.04-270 (1.28-3.23) | 2.61, 0.05-780 (1.54-4.43) | 8.80, 0.05-940 (5.21-14.87) |
| Living room | 1.30, 0.04-120.0 (0.85-1.98) | 11.63, 0.05-2150 (6.59-20.54) | 17.08, 0.05-1870 (9.49-30.74) |
Allergen sensitization, lung function, eNO, and airway reactivity
There was no difference in percent predicted FEV1 between subjects sensitized to at least one allergen and nonsensitized subjects (mean [95% CI], 87.4% [84.7%-90.0%] vs 88.3% [82.8%-93.8%], P = .77). However, sensitized subjects had significantly lower PD20 FEV1 values than nonsensitized subjects (GM [95% CI], 0.37 mg [0.28-0.49 mg] vs 1.28 mg [0.63-2.59 mg]; GM ratio, 3.5-fold; 95% CI, 1.62 to 7.35; P = .002). eNO was significantly greater in sensitized compared with nonsensitized subjects (GM [95% CI], 11.6 ppb [10.3-13.0 ppb] vs 7.2 ppb [5.7-9.2 ppb]; GM ratio, 1.6-fold; 95% CI, 1.2-2.1; P = .001).
Subjects were divided into one of the following 4 groups on the basis of their sensitization and exposure status to any of the allergens: (1) not sensitized and not exposed to any study allergens (NS/NE); (2) sensitized but not exposed to any study allergens (S/NE); (3) not sensitized but exposed to any study allergens (NS/E); and (4) sensitized and exposed to 1 or more specific allergens (S/E).
The mean dose of inhaled steroid was 1043 μg (95% CI, 645-1440 μg) for the NS/NE group, 660 μg (95% CI, 583-738 μg) for the S/NE group, 830 μg (95% CI, 690-971 μg) for the NS/E group, and 632 μg (95% CI, 539-724 μg) for the S/E group (S/E vs NS/NE, P < .01).
Effect of sensitization and exposure on pulmonary function test results and eNO
When sensitization and exposure to all allergens was considered in the ANOVA, there was a significant difference between the groups for PD20, eNO, and FEV1 percent predicted. Subjects in the S/E group had significantly lower FEV1 percent predicted values (mean difference, 5.6; 95% CI, 0.6-10.6; P = .029), greater BR (GM ratio, 2.9; P < .001), and higher eNO values (GM ratio, 0.7; P = .001) than the rest of the patients in the other groups combined (Table III).
Table III. Analysis of pulmonary function in relation to allergen sensitization and exposure status
| Mean GM (95% CI) | Overall ANOVA | S/E vs all other subgroups | 2-Sample t test | ||||
|---|---|---|---|---|---|---|---|
| NS/NE | S/NE | NS/E | S/E | Linear contrast | |||
| FEV1 % predicted | (n = 21) 92.9 (85.2-100.6) | (n = 73) 86.9 (81.9-92.0) | (n = 61) 90.8 (85.9-95.7) | (n = 118) 83.7 (79.6-87.7) | F(3,269) = 2.2; P = .086 | t(269) = 2.4; P = .018 | t(271) = 2.2; P = .029; mean = 83.7 vs 89.3; mean difference = 5.6; 95% CI = 0.6-10.6 |
| PD20 | (n = 15) 0.70 (0.29-1.72) | (n = 47) 0.54 (0.32-0.90) | (n = 31) 1.03 (0.53-1.97) | (n = 65) 0.25 (0.16-0.37) | F(3,154) = 5.7; P = .001 S/E significantly lower than NS/E | t(154) = 3.8; P < .001 | t(156) = 3.8; P < .001; GM = 0.25 vs 0.70; mean ratio difference = 2.9; 95% CI = 1.6-4.8 |
| eNO | (n = 20) 6.8 (4.9-9.4) | (n = 59) 11.2 (9.2-13.6) | (n = 57) 7.8 (6.1-9.9) | (n = 104) 12.9 (10.9-15.3) | F(3,236) = 6.3; P = .001, S/E significantly higher than NS/E and NS/NE | t(236) = 3.7; P < .001 | t(238) = 3.3; P = .001; GM = 12.9 vs 8.9; mean ratio difference = 0.7; 95% CI = (0.6-0.9) |
Table IV. Lung function outcomes, sensitization, and exposure to individual allergens
| Mean GM (95% CI) | Overall ANOVA | S/E vs all other subgroups | 2-Sample t test | ||||
|---|---|---|---|---|---|---|---|
| NS/NE | S/NE | NS/E | S/E | Linear contrast | |||
| Dust mite | |||||||
| FEV1 % predicted | (n = 59) 91.4 (86.8-96.3) | (n = 93) 86.1 (81.5-90.8) | (n = 57) 89.1 (83.7-94.6) | (n = 81) 84.0 (79.3-88.7) | F(3,286) = 1.6; P = .18 | t(286) = 1.8; P = .08 | t(288) = 1.6; P = .11; mean = 84.0 vs 88.4; mean difference = 4.4; 95% CI = −1.0 to 9.8 |
| PD20 | (n = 41) 0.92 (0.52-1.60) | (n = 58) 0.36 (0.23-0.57) | (n = 27) 0.45 (0.22-0.93) | (n = 45) 0.26 (0.16-0.42) | F(3,167) = 4.1; P = .008 | t(167) = 2.4; P = .02 | t(169) = 2.2; P = .027; GM = 0.26 vs 0.51; mean ratio difference = 1.99; 95% CI = 1.1 to 3.6 |
| eNO | (n = 54) 7.7 (6.0-10.0) | (n = 80) 11.2 (9.4-13.3) | (n = 54) 10.4 (8.2-13.0) | (n = 68) 13.0 (10.2-16.4) | F(3,252) = 3.6; P = .015 | t(252) = 2.4; P = .02 | t(254) = 2.2; P = .03; GM = 13.0 vs 9.8; mean ratio difference = 0.76; 95% CI = 0.59 to 0.97 |
| Cat | |||||||
| FEV1 % predicted | (n = 114) 88.3 (84.5-92.1) | (n = 100) 89.3 (85.4-93.1) | (n = 37) 87.8 (79.9-95.8) | (n = 42) 80.6 (73.2-88.0) | F(3,289) = 1.8; P = .15 | t(289) = 2.2; P = .03 | t(291) = 2.3; P = .023; mean = 80.6 vs 88.6; mean difference = 8.0; 95% CI = 1.1 to 14.9 |
| PD20 | (n = 65) 0.54 (0.35-0.83) | (n = 65) 0.33 (0.22-0.52) | (n = 22) 1.26 (0.58-2.75) | (n = 22) 0.21 (0.10-0.42) | F(3,170) = 4.9; P = .003 | t(170) = 2.6; P = .009 | t(172) = 2.1; P = .034; GM = 0.21 vs 0.50; mean ratio difference = 2.37; 95% CI = 1.1 to 5.2 |
| eNO | (n = 102) 9.0 (7.6-10.8) | (n = 35) 13.0 (10.7-15.8) | (n = 35) 6.9 (5.2-9.1) | (n = 39) 14.8 (11.6-19.0) | F(3,253) = 7.5; P < .001 | t(253) = 3.0; P = .003 | t(255) = 2.6; P = .010; GM = 14.8 vs 9.9; mean ratio difference = 0.67; 95% CI = 0.49 to 0.91 |
| Dog | |||||||
| FEV1 % predicted | (n = 132) 89.8 (86.1-93.5) | (n = 90) 86.0 (81.6-90.4) | (n = 41) 89.3 (83.6-95.0) | (n = 42) 78.2 (69.7-86.6) | F(3,288) = 2.7; P = .048 | t(288) = 2.4; P = .015 | t(290) = 2.5; P = .013; mean = 78.2 vs 88.4; mean difference = 10.2; 95% CI = 2.2 to 18.3 |
| PD20 | (n = 83) 0.63 (0.42-0.94) | (n = 56) 0.34 (0.22-0.52) | (n = 24) 0.32 (0.15-0.71) | (n = 10) 0.24 (0.08-0.70) | F(3,169) = 2.1; P = .097 | t(169) = 0.9; P = .37 | t(171) = 1.1; P = .28; GM = 0.24 vs 0.46; mean ratio difference = 1.89; 95% CI = 0.60 to 5.97 |
| eNO | (n = 120) 9.1 (7.8-10.7) | (n = 73) 13.5 (11.1-16.3) | (n = 36) 9.5 (6.6-13.6) | (n = 28) 11.6 (8.3-16.3) | F(3,253) = 3.2; P = .024 | t(253) = 0.5; P = .59 | t(255) = 0.6; P = .54; GM = 11.6 vs 10.4; mean ratio difference = 0.90; 95% CI = 0.63 to 1.28 |
Results of the ANOVA model with the main factors of sensitized versus not sensitized and exposed versus not exposed and the interaction of sensitized versus not sensitized × exposed versus not exposed together with the potential confounding factors, assessing the independent effects of sensitization and exposure, are presented in Table V.
Table V. Independent effects of sensitization and exposure by using an ANOVA model together with the potential confounding factors of age, sex, family history of asthma, smoking history, and use of inhaled steroids
| Sensitization | Exposure | Interaction | |
|---|---|---|---|
| FEV1 % predicted | |||
| Overall | P = .057 | P = .62 | P = .12 |
| Significant confounders: age, P < .001; sex, P < .001; inhaled steroids, P = .029 | |||
| Mite | P = .003 | P = .70 | P = .75 |
| Significant confounders: age, P < .001; sex, P = .001; inhaled steroids, P = .019 | |||
| Cat | P = .014 | P = .43 | P = .12 |
| Significant confounders: age, P < .001; sex, P = .001; inhaled steroids, P = .036 | |||
| Dog | P = .014 | P = .52 | P = .18 |
| Significant confounders: age, P < .001; sex, P = .001 | |||
| PD20 | |||
| Overall | P = .005 | P = .35 | P = .048 |
| Significant confounder: family history, P = .04 | |||
| Mite | P = .009 | P = .72 | P = .47 |
| Significant confounder: age, P = .05 | |||
| Cat | P = .002 | P = .25 | P = .038 |
| Significant confounder: age, P = .05 | |||
| Dog | P = .44 | P = .56 | P = .88 |
| Significant confounder: age, P = .016 | |||
| eNO | |||
| Overall | P = .025 | P = .87 | P = .18 |
| Significant confounders: age, P = .02; smoker, P = .003 | |||
| Mite | P = .079 | P = .06 | P = .81 |
| Significant confounders: age, P = .018; smoker, P < .001 | |||
| Cat | P < .001 | P = .41 | P = .37 |
| Significant confounder: smoker, P = .002 | |||
| Dog | P = .021 | P = .53 | P = .93 |
| Significant confounders: age, P = .028; smoker, P = .001 |
There was no significant difference in the numbers of subjects classified as having normal, mild, moderate, or severe BR between the subjects who underwent histamine challenge compared with methacholine challenge or in the PD20 (GM [95% CI], 0.40 mg [0.28-0.56 mg] vs 0.52 mg [0.34-0.77 mg]; histamine vs methacholine challenge, P = .33). The combined analyses adjusted for the method of challenge showed no effect of the method on the outcomes, and no interaction was seen between the method and any of the sensitized-exposed groups or with the S/E group versus the rest of the groups. These data suggest dose equivalence between the 2 challenge methods.
Discussion
This is one of the first large studies assessing the influence of both sensitization and exposure to indoor allergens on the severity of asthma, as measured on the basis of pulmonary function tests, BR, and eNO. In a cohort of more than 300 asthmatic subjects with disease of varied severity, we have demonstrated significantly lower FEV1 values, higher levels of eNO, and increased BR in subjects who were both sensitized and exposed to sensitizing allergen compared with that seen in other subjects. Furthermore, there was a significant interaction between sensitization and exposure to any allergen and between sensitization and exposure to cat allergen for nonspecific BR but not eNO or baseline pulmonary function. Of the potential confounding factors, age was the most common significant associate for all measures. Smoking history was associated with a lower eNO value, and male sex and inhaled steroid use were associated with lower FEV1 values.
Several studies19, 20, 21 have reported an association between the risk of admission to the hospital with acute asthma and allergic sensitization, but the relationship between atopy and progressively severe asthma is less well proved. Studies in the general population have shown a relationship between FEV1 decline and the presence of atopy,22, 23 whereas a study in asthmatic patients24 did not demonstrate this effect. One study25 actually showed a greater decline in lung function in nonatopic asthmatic subjects.
The relationship between eNO and atopy has been less studied. Two studies26, 27 have demonstrated increased eNO values in atopic subjects aged 5 to 15 years compared with nonatopic asthmatic patients but no difference between atopic and nonatopic (ie, nonasthmatic) control subjects. Epithelial cells of asthmatic subjects show greater expression of inducible NO synthase,28 and this suggests that the airway epithelial lining might differ between atopic and nonatopic subjects and that this difference is greater in asthmatic subjects.
Several studies have suggested that exposure to allergens worsens asthma control. Allergen avoidance studies have demonstrated an improvement in BR and symptoms.29 We have previously reported a relationship between mite allergen exposure and clinical activity of asthma (measured by level of BR, peak flow variability, and FEV1 percent predicted).30 A case-control study31 demonstrated that the incidence of sensitization and exposure to indoor allergens was significantly greater in subjects with brittle asthma compared with that in subjects with stable asthma. A study in patients with mild asthma (not taking inhaled steroids)32 showed higher eNO values in subjects sensitized and exposed to allergens compared with that in subjects sensitized but not exposed to allergens. Also, allergen avoidance has been associated with decreases in eNO values,33 and, in an experimental study, an increase in eNO after allergen challenge.34 In the current study subjects who were both sensitized and exposed to high levels of the sensitizing allergen had more severe asthma, as measured on the basis of eNO, BR, and FEV1 than subjects who were not sensitized and exposed. However, in the case of eNO, the lack of interaction between sensitization and exposure could suggest that the effect was predominantly caused by sensitization, whereas for BR there was a significant interaction between sensitization and chronic exposure in the home.
When exposure and sensitization to individual allergens was examined in the present study, a significant difference was seen for FEV1 percent predicted between the subjects sensitized and exposed to either cat and dog allergen and the rest of the group. In a previous study in children,35 there was a trend toward lower lung function in subjects sensitized to these allergens, and sensitivity to dog had the strongest effect on BR. This latter finding was not seen in our study. Analysis of exposure and sensitization to individual allergens was also performed in a study in children in the United States.36 This study demonstrated greater asthma morbidity in subjects exposed and sensitized to cockroach allergen. This finding did not occur with exposure to dust mite or cat allergen. However, the percentage of subjects considered to be exposed to high levels of dust mite (9.7%) and cat allergen (12.6%) was considerably lower than that seen in our study.
Some subjects in our study did not have a bronchial challenge. Most of these subjects' lung functions precluded the test, and some refused the investigation. It is recognized that this could theoretically influence the results. However, because there was no difference in the frequency of sensitized and exposed subjects in the 2 groups, it is presumed that the comparison of BR between the S/E group and the rest of the subgroups is valid.
In conclusion, our study has shown that asthmatic patients who are sensitized to at least one allergen have evidence of more severe asthma, as measured on the basis of eNO and BR. Furthermore, markers of asthma activity within the sensitized group are significantly worse in those subjects who are also exposed to the allergens causing sensitization.
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☆ Reprint requests: Stephen J. Langley, MD, MBA, Medicines Evaluation Unit, North West Lung Centre, Wythenshawe Hospital, Manchester, M23 9LT, United Kingdom.
PII: S0091-6749(03)01625-7
doi:10.1067/mai.2003.1654
© 2003 Mosby, Inc. All rights reserved.
Volume 112, Issue 2 , Pages 362-368, August 2003
