1. Introduction
Asthma is a chronic inflammatory lung disease with a large global burden [
1,
2,
3]. A complex genetic disorder, asthma results from the interplay of multiple genetic variants with environmental factors [
4,
5,
6,
7]. Numerous genes associated with asthma susceptibility have been identified through candidate gene analyses and genome-wide linkage or association studies [
7,
8]. Recent studies highlight the importance of genetic variants of innate immune pathways [
9,
10,
11] as well as gene–environment interactions (GEI) [
4,
7,
12,
13,
14,
15].
Members of the IL1 family participate in inflammation with well-established biological plausibility for an association between IL1 family genes and asthma or related phenotypes [
16,
17,
18,
19]. The IL1 signaling pathway involves the IL1 receptor type I (IL1R1), through which IL1α and IL1β induce a pro-inflammatory response. The interleukin-1 receptor antagonist (
IL1RN) gene encodes the IL1 antagonist protein, IL1RA, which competitively binds to IL1R1 but does not elicit the downstream signal transduction cascade [
18,
19]. The pro-inflammatory effect of IL1 and the anti-inflammatory effect of IL1RA in asthma have been documented in human and animal functional and mechanistic studies [
20,
21,
22,
23,
24,
25,
26,
27]. Both IL1β and IL1RA are increased in bronchoalveolar lavage fluid during asthma exacerbations in humans [
23]. IL1 is involved in the interaction between house dust mites and the innate immune response leading to allergic sensitization [
28]. IL1RA also attenuates airway hyper-responsiveness following exposure to ozone [
26]. It is known that even a small modification in the
IL1RN gene has the potential to alter inflammatory and immune functions mediated by IL1 binding [
18].
Several genome-wide linkage studies and genome-wide association studies (GWAS) suggest that the human chromosome region 2q122–q14 containing the IL1 cluster harbors candidate genes for asthma and other inflammatory diseases [
10,
29,
30,
31,
32,
33,
34,
35,
36,
37,
38]. Associations between single nucleotide polymorphisms (SNPs) in
IL1RN and asthma were first identified by Gohlke et al. in parent-affected child trios from Germany and Sweden and replicated using an independent cohort of trios from Italy [
39]. The design of the study was very robust in avoiding population stratification and the data analyses were careful and thorough. Thus the reported association finding was highly trustworthy, supported by animal and mechanistic studies [
24,
40]. Moreover, the association between
IL1RN variants and asthma was reaffirmed independently by Pattaro et al. in an adult German population-based sample [
41]. The studied SNPs in
IL1RN are in strong linkage disequilibrium (LD) [
39]. Importantly, in the adult population, carriers of a common haplotype of
IL1RN involving the common allele “A” in SNP rs2234678 have a high prevalence of doctor-diagnosed asthma (odds ratio OR = 3.12, p = 0.007) [
41], in line with findings in pediatric cohorts studied by Gohlke et al. [
39] These reported findings suggest that the minor allele “G” and rare genotype GG at SNP rs2234678 would be protective for asthma.
In contrast to these studies, Ramadas et al. reported that the rare genotype GG at rs2234678 carried a significant risk for asthma in a group of children with exposure to maternal smoking during pregnancy (OR = 4.43, p = 0.004) [
14]. Thus, the large ORs in these reported studies diverge in opposite directions with the genotype rs2234678 GG carrying a protective effect for asthma in adults [
39,
41] but a significant risk for asthma in a subgroup of children with passive exposure to tobacco smoke and maternal smoking during pregnancy [
14]. The dataset reported in Ramadas et al. was from a well-designed longitudinal cohort study of children who were evaluated up to 10 years old in the United Kingdom. The reported large OR for early onset asthma is likely reproducible. Consequently, these seemingly inconsistent findings between Ramadas et al. and Pattaro et al. highlight an unaddressed important knowledge gap on the impact of
IL1RN variants on asthma susceptibility in the context of possible gene-environment interactions (GEI). In addition to potential GEI, there is also a knowledge gap between genotypic and haplotype-based SNP analyses. It is well known that genotype of a tag SNP is directly observable and straightforward for analysis, however, the genotype of a tag SNP is likely in LD with a functional variant but itself is unlikely to have direct biological functions. While long haplotypes are likely harboring functional polymorphisms, unfortunately, the linkage phase between SNPs is often ambiguous and the haplotypes cannot be directly observed in typical association studies. It is thus of some importance to infer haplotypes using suitable statistical techniques and reconcile the haplotype findings with more direct genotypic SNP analysis.
Environmental tobacco smoke (ETS) or passive exposure to tobacco smoke is a well-known risk factor for the development of asthma [
42,
43,
44] and exacerbates asthma symptoms in children and adults [
44,
45,
46,
47]. ETS is also an important environmental exposure when assessing genetic susceptibility of asthma [
6,
12,
13,
14,
15,
48]. It is possible that the lungs and immune system of children are more susceptible to injuries due to the local environment including childhood ETS because they are not fully developed. Maternal smoking as studied in Ramadas et al. may attenuate innate immune function in the neonatal period [
49], making this a vulnerable time for gene and environment interactions. Epigenetic changes that occur in early life may also contribute to genetic differences in pediatric asthma susceptibility to ETS [
50]. However, the GEI or differential association of childhood ETS exposure and risk for asthma or early onset asthma within various
IL1RN genotype groups has not been reported. The New York University/Bellevue Asthma Registry (NYUBAR) was designed for case-control studies using an admixed urban adult population with a focus on severe asthma [
51,
52] and collected information on childhood ETS exposure and age at asthma onset. Thus, our main goal was to identify the gene–environment interaction of childhood ETS exposure with
IL1RN variants and asthma risk and evaluate the impact of GEI on the risk of asthma and early onset asthma to bridge the knowledge gap in understanding the seemingly diverging effects of some rare
IL1RN genotypes on asthma susceptibility, in contrast to haplotype-based findings in existing cohort studies. A final issue to be addressed is that Pattaro et al. considered asthma in an adult cohort while Ramadas et al. studied pediatric or early-onset asthma for subjects with childhood ETS. At NYUBAR, we have adult asthmatics with information on both childhood ETS exposure and age of onset for asthma, thus we also aimed to bridge the findings on significant protective effect of GG in SNP 2234678 on adult asthma as well as high risk effect on early onset asthma in the presence of childhood ETS exposure.
4. Discussion
Genotypic/haplotype analyses of the tag SNPs in
IL1RN and asthma susceptibility for the NYUBAR population as a whole resulted in findings that were in accordance with previous publications using different analyses and independent cohorts [
39,
41,
67]. Our data support the evidence of the protective effects of some SNP alleles and haplotypes for asthma previously identified in other cohorts [
39,
41,
67]. Importantly, our analyses indicated that these protective effects of these tag SNP polymorphisms were significant only within the groups without childhood ETS exposure and in fact, these polymorphisms became risk variants for early onset asthma in the subgroup exposed to childhood ETS. The latter finding is consistent with the findings of Ramadas et al. [
14] using a cohort from the United Kingdom. Our data, therefore, suggest that childhood ETS exposure modifies the
IL1RN haplotype/genotype-dependent risk for asthma susceptibility and bridge a knowledge gap and explain previous discordant study results on GEI between variants of
IL1RN and ETS exposure in asthma studies.
Numerous studies suggest that the asthma risk of genetic variants might be modified in the presence of environmental factors such as ETS exposure [
12,
13,
14,
68]. Linkage studies indicate that multiple chromosomal regions, including the 2q region harboring the IL1 cluster, contain risk variants that make carriers of these variants who are exposed to ETS more susceptible to asthma [
12,
13]. When stratified by genotypes of
IL1RN and focused on subjects with rare homozygous genotypes of
IL1RN, we found that childhood ETS exposure elevated the risk for early onset asthma. When stratified by childhood ETS exposure, those with childhood ETS and the rare homozygous genotype of
IL1RN had a higher risk for early onset asthma compared to those with common genotypes in multivariate analysis. In particular, the finding of a higher risk of early onset asthma for carriers of rs2234678 GG versus rs2234678 GA/AA (OR = 4.467, p = 0.021) is consistent with the increased risk in children with maternal ETS exposure (OR = 4.43, p = 0.004) reported by Ramadas et al. [
14] In addition, the finding of a much higher risk of early onset asthma for carriers of rs2234678 GG in the childhood ETS exposed group is in striking contrast to our data in those without childhood ETS, in which the rare genotype GG at rs2234678 was significantly associated with a smaller risk of asthma susceptibility (OR = 0.215, p = 0.021). These results are in support of published results of Pattaro et al. [
41] who studied an adult German population-based sample and reported that carriers of a common haplotype of
IL1RN involving the common allele “A” in SNP rs2234678 have a high prevalence of doctor-diagnosed asthma. Thus the finding of Pattaro et al.
41 would imply GG in SNP rs2234678 would have a protective effect as indicated in
Table 3 in the group without ETS exposure for asthma.
The finding in the stratified analysis of
IL1RN variants with odds ratios in opposite directions reinforces the importance of accounting for both environmental exposures and GEI in risk analyses for asthma. The findings suggest that in such situations, association analyses that ignore environmental exposures and GEI can potentially lead to false negatives or overly conservative p-values. This is illustrated by the genotypic association analysis of SNP rs2234678 in
Table 3 and
Table 5. The sample size for the group without ETS exposure (N = 211) is much smaller than the overall sample size N = 441, however, the p-value is significant among those without childhood ETS (p = 0.021,
Table 3), but is not significant in the overall group (N = 441) for SNP rs2234678 (p = 0.07,
Table 5). Similarly, GWAS without considering GEI can also miss allelic associations. In addition, analyses that do not adjust for environmental exposure can easily cause confusion and paradoxical findings. For example, from
Table 5, the nonstratified analysis (N = 441) found a nonsignificant protective effect (OR = 0.459, p = 0.07) for rs2234678 GG, which in fact merely reflected the significant effect among subjects without ETS exposure (OR = 0.215, p = 0.021) as reported in
Table 3. On the other hand, rs2234678 GG was found to be a nonsignificant risk genotype (OR = 1.788, p = 0.203) for early onset asthma in nonstratified analysis, which merely reflected the significant effect among subjects with childhood ETS exposure (OR = 4.467, p = 0.021,
Table 3). Furthermore, in the nonstratified analysis for the overall group (N = 441), using SNP rs2234678 as an example, the OR of the rare genotype GG was less than one for susceptibility to asthma (
Table 5, neither adjusting for ETS nor GEI) whereas it was larger than one for susceptibility to early onset asthma (data not shown). Similar results hold for other SNPs. This paradox illustrates the potential confusion which can be caused by failing to account for important environmental risk factors such as ETS.
The divergent findings of an elevated risk for the interaction between
IL1RN genotypes and childhood ETS for early onset asthma but not for asthma in the total population have precedent in the literature on childhood predisposition to asthma. The linkage associations between the “Th2” cytokine gene cluster and asthma susceptibility have been suggested to be more evident in children exposed to tobacco smoke [
12,
13]. Divergent effects of exposures have been shown for CD14 and pets with ETS exposure [
69]. Although we have not examined potential explanations for the age change in susceptibility, the possibility exists that the lungs and immune system of children are more susceptible to injuries due to the environment including childhood ETS because they are not fully developed. Maternal smoking may attenuate innate immune function in the neonatal period [
49], making this a vulnerable time for gene and environment interactions. Epigenetic changes that occur in early life may also contribute to genetic differences in susceptibility to ETS [
50]. Recent studies on CD14, in which divergent effects have also been shown, suggest that the presence of pets and ETS limit the increase in CD14 methylation that occurs before age 10 years and this has been suggested as a partial explanation for the diverging CD14 allele associations with allergic diseases detected in different environments [
70].
Studies on GEI can have significant implications for public health. Childhood ETS exposure was a risk factor for early onset asthma for our study population regardless of genotypes even after adjustment for many covariates. Moreover, childhood ETS exposure led to significant elevation of risk for early onset asthma for the subpopulation who carried rare genotypes of the tag SNPs of
IL1RN including the GG genotype in SNP rs2234678. Childhood ETS exposure was about 52% in our study cohort, consistent with current estimates suggesting that 55% of children have detectable levels of serum cotinine [
71]. Given that childhood ETS exposure is the most common but preventable childhood environmental hazard, our findings reinforce the impact of childhood ETS exposure on early onset asthma.
The use of an admixed population can complicate genetic analyses. We accounted for population admixture with the use of ancestral markers and after adjustment for population admixture, our findings were consistent with previous studies that did not have the potential biases of population stratification when using the transmission disequilibrium/test (TDT) with parents-affected child trios. After adjusting for age, BMI, gender, and ancestral information, many rare haplotypes of
IL1RN tagging SNPs rs2234678-rs392503-rs1794067-rs973635-rs440286 (e.g., GGAGA) had protective effect for asthma relative to the more common haplotype AAGGC in either the overall population or subjects without childhood ETS exposure. The haplotype AAGGC is more common than other haplotypes, but its frequency is less than 50%. This finding was consistent with previously published reports [
39], suggesting that the finding was robust across different ancestries. Moreover, we previously replicated genetic and asthma phenotype studies with this population [
52,
53], supporting the robustness of this population for asthma analyses.
There are several potential limitations to this study. We recruited an adult population and did not have extra information to confirm childhood ETS exposure (i.e., cotinine measurements), thus the responses about the exposure to childhood ETS may be subject to recall bias. However, childhood ETS exposure is about 52% in our study cohort, which is consistent with current estimates suggesting that 55% of children have detectable levels of serum cotinine [
71]. We do not have information about in utero tobacco exposures. We suspect some of those with childhood ETS exposure might have maternal smoking during pregnancy as studied in Ramadas et al. [
14], but we do not have that information. A similar potential for recall bias exists for age of onset of disease. We used physician diagnosis to determine age of onset of asthma, however, asthma symptoms may pre-exist age of diagnosis. These biases would not be expected to differ systematically between the comparison groups. We selected a cut point of age 10 as early onset asthma to be comparable with previous studies of
IL1RN [
14]. However, the use of any cutoff point between ages 8 and 12 years did not affect the association results of our analysis (
Table A1), suggesting that the analysis method we employed was robust against potential recalling errors on age of onset. Finally, after stratification for ETS, our rare genotype groups became quite small. It is possible that epigenetic mechanisms are involved in the gene–environment interaction in the context of childhood ETS exposure, unfortunately, we do not have data on epigenetic mechanisms for the study. Our ability to identify a strong OR in the subpopulations, suggested that the effect of the association was quite strong, a finding that is consistent with the fact that both Pattero et al. and Ramadas et al. found strong effect sizes (large ORs). Nevertheless, we recognize the desirability for additional replication in even larger samples for the GEI finding.