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Associations of Pet Ownership with Wheezing and Lung Function in Childhood: Findings from a UK Birth Cohort

  • Simon M. Collin,

    Affiliations Centre for Child & Adolescent Health, University of Bristol, Bristol, United Kingdom, School of Social & Community Medicine, University of Bristol, Bristol, United Kingdom

  • Raquel Granell,

    Affiliation School of Social & Community Medicine, University of Bristol, Bristol, United Kingdom

  • Carri Westgarth,

    Affiliations Department of Epidemiology & Population Health, University of Liverpool, Liverpool, United Kingdom, School of Veterinary Science, University of Liverpool, Liverpool, United Kingdom

  • Jane Murray,

    Affiliation School of Veterinary Sciences, University of Bristol, Bristol, United Kingdom

  • Elizabeth S. Paul,

    Affiliation School of Veterinary Sciences, University of Bristol, Bristol, United Kingdom

  • Jonathan A. C. Sterne,

    Affiliation School of Social & Community Medicine, University of Bristol, Bristol, United Kingdom

  • A. John Henderson

    Affiliation School of Social & Community Medicine, University of Bristol, Bristol, United Kingdom

Associations of Pet Ownership with Wheezing and Lung Function in Childhood: Findings from a UK Birth Cohort

  • Simon M. Collin, 
  • Raquel Granell, 
  • Carri Westgarth, 
  • Jane Murray, 
  • Elizabeth S. Paul, 
  • Jonathan A. C. Sterne, 
  • A. John Henderson



Asthma is a heterogeneous condition and differential effects of pet ownership on non-atopic versus atopic asthma have been reported. The aim of this study was to investigate whether pet ownership during pregnancy and early childhood was associated with wheezing from birth to age 7 years and with lung function at age 8 years in a UK population-based birth cohort.


Data from the Avon Longitudinal Study of Parents and Children (ALSPAC) were used to investigate associations of pet ownership at six time-points from pregnancy to age 7 years with concurrent episodes of wheezing, wheezing trajectories (phenotypes) and lung function at age 8 years using logistic regression models adjusted for child’s sex, maternal history of asthma/atopy, maternal smoking during pregnancy, and family adversity.


4,706 children had complete data on pet ownership and wheezing. From birth to age 7 years, cat ownership was associated with an overall 6% lower odds of wheezing (OR=0.94 (0.89-0.99)). Rabbit and rodent ownership was associated with 21% (OR=1.21 (1.12-1.31)) and 11% (OR=1.11 (1.02–1.21)) higher odds of wheezing, respectively, with strongest effects evident during infancy. Rabbit and rodent ownership was positively associated with a ‘persistent wheeze’ phenotype. Pet ownership was not associated with lung function at age 8 years, with the exception of positive associations of rodent and bird ownership with better lung function.


Cat ownership was associated with reduced risk, and rabbit and rodent ownership with increased risk, of wheezing during childhood. The mechanisms behind these differential effects warrant further investigation.


Asthma during childhood has a considerable impact on quality-of-life and healthcare costs [1,2]. A child’s susceptibility to asthma is likely to be determined by interacting genetic and environmental factors [3,4]. Ownership of household pets has attracted attention as an early-life environmental exposure which might play a role in the development of asthma and allergy. Pet ownership is common among households in countries where the incidence and prevalence of childhood asthma and allergies have changed substantially over the past few decades [5,6].

We reported previously that family ownership of domestic pets during early life, including during the pre-natal period, was associated with lower odds of atopic asthma by mid-childhood compared with no pet ownership [7], confirming findings from previous studies [810]. Conversely, we also found that pet ownership, particularly of rabbits and rodents, tended to be associated with higher odds of non-atopic asthma. These differential effects of pet ownership probably reflect heterogeneity within childhood asthma, which is recognized to be a complex condition characterised by distinct phenotypes [11], as suggested by analysis of trajectories of wheezing through childhood [12,13]. Differential associations of early-life environmental exposures with wheezing phenotypes, and with phenotypic traits such as lung function, may provide clues as to distinct environmental and pathophysiological processes in asthma causation and exacerbation [14].

Here we used data from the Avon Longitudinal Study of Parents and Children (ALSPAC), a well-characterised UK-based birth cohort, to investigate associations of pet ownership (any pet and specific pet types) at six time-points (from pregnancy to age 7 years) with episodes of wheezing reported at annual intervals from 6 months to 7 years of age, with longitudinal wheezing phenotypes [12], and with lung function (Forced Expiratory Volume in 1 second (FEV1) and Forced Vital Capacity (FVC)) measured at age 8 years.


Study population

The Avon Longitudinal Study of Parents and Children (ALSPAC) is a UK population-based study which aims to investigate environmental and genetic influences on the health and development of children [15]. Pregnant women residing in the former Avon Health Authority in south-west England who had an estimated date of delivery between 1 April 1991 and 31 December 1992 were invited to take part, resulting in a cohort of 14,541 pregnancies and 13,978 children alive at 12 months of age (excluding triplets and quads). The primary source of data collection was via self-completion questionnaires sent to mothers at four time-points during pregnancy then at approximately annual intervals following birth. The representative nature of the ALSPAC sample has been investigated by comparison with the 1991 National Census data of mothers with infants under 1 year of age who were residents in the county of Avon. The ALSPAC sample had a slightly greater proportion of mothers who were married or cohabiting, who were owner-occupiers and who had a car in the household. The study had a smaller proportion of ethnic minority mothers. Data used for this submission will be made available on request to the ALSPAC executive committee ( The ALSPAC data management plan describes in detail the policy regarding data sharing, which is through a system of managed open access (

Ethical approval

Ethical approval for this study was obtained from the ALSPAC Ethics and Law Committee (IRB00003312). Ethical approval for the ‘Focus@8’ research clinics was granted by Weston Local Research Ethics Committee (NHS LREC ref. E177, 21st September 1999). Informed written consent was obtained from the original participants and from the parent(s), next of kin, caretakers, or guardians on behalf of the minors/children enrolled in ALSPAC.


Episodes of wheeze and wheezing phenotypes.

Parental reports of child wheezing were obtained from questionnaires sent to the mothers at annual intervals from 6 months to 7 years of age (at approximate ages 6, 18, 32, 42, 54, 69, and 81 months). Presence of wheeze was based on a positive response to the question “In the past 12 months has (your child) had wheezing with whistling on the chest?” or a reported occurrence of wheeze within a list of 15 common symptoms. As previously described, these data were used in a longitudinal latent class analysis to define phenotypes of childhood wheezing, resulting in 6 wheezing phenotypes that were labelled ‘never/infrequent’, ‘transient early’, ‘prolonged early’, ‘intermediate-onset’, ‘late-onset’ and ‘persistent wheezing’ [12].

Lung function.

Lung function was measured by spirometry according to American Thoracic Society criteria [16] in ‘Focus@8’ research clinics to which all participants were invited at age 8 years (median 103, range 89 to 127 months). Forced expiratory volume in 1 second (FEV1) and forced vital capacity (FVC) were converted to units of sex-, age- and height-adjusted standard deviations (z-scores) [17].


Pet ownership.

Pet ownership questions were asked (in questionnaires about the mother and her environment) during pregnancy (up to 28 weeks gestation) and at child ages of 8 months and 2, 3, 4, and 7 years. The carer of the child (usually the mother) was asked ‘do you have any pets’ and ‘how many of the following pets do you have’. Pet types included cats, dogs, rabbits, rodents (mice, hamster, gerbil etc.), and birds. For the purpose of our study, we defined 4-level categorical variables to indicate whether a cat, dog, rabbit, rodent, bird, or any pet, had been owned/acquired as follows: “Never”; “At age 3 years or later, not before” (owned at age 33 months or at any time thereafter, but not at age 21 months or at any time before, including during pregnancy); “Before and after age 3 years” (owned at any time before age 33 months, including during pregnancy, and at any time thereafter, referred to as ‘continuous’ ownership); “Before but not after 3 years” (owned at any time before, including during pregnancy, but no longer owned at age 33 months or at any time thereafter). We chose age 3 years as a meaningful time point for the acquisition of pets because we wanted to isolate potential reverse-causality in associations of pet ownership with asthma and atopy, specifically, discontinuation of ownership due to the emergence of asthma or atopy during infancy or early childhood [18]. We also defined a binary exposure of “ever” or “never” having owned any pet and specific pet types. Ownership of fish, turtles and tortoises was recorded from age 2 years onwards, and was not coded as a 4-level categorical exposure variable included in the ‘any’ pet ownership binary exposure variable.

Other variables

Potential confounders.

A composite ‘family adversity’ index and three factors previously reported to be associated with wheezing phenotypes in ALSPAC (sex of child, maternal history of asthma or allergy, and maternal smoking during pregnancy) [14] were investigated as potential confounders of the association between exposures and outcomes. Maternal history of asthma or allergy was a binary variable derived from responses to an antenatal (18 – 20 weeks gestation) questionnaire in which the mother was asked: a) “Have you ever had any of the following problems?” with responses for “Asthma” of “Yes had it recently” or “Yes in past, not now” coded as ‘yes’; and b) “Would you say that you were allergic to anything?”, with affirmative responses to any of “cat”, “pollen”, “dust”, “insect stings or bites”, or “something else” coded as ‘yes’. Maternal smoking during pregnancy was a binary variable derived from responses to questions put to the mother in an antenatal and a postnatal questionnaire, asking whether the mother had smoked in the first 3 months of the pregnancy, at the mid-point (18 – 20 weeks), or in the last 2 months of the pregnancy.

Family Adversity Index.

The standard ALSPAC Family Adversity Index (FAI) is derived from responses to questions asked during pregnancy about the following 10 factors, comprising 18 items in total: 1) age of mother at first pregnancy; 2) housing, comprising a) adequacy, b) basic amenities, c) defects, damp, infestation; 3) mother’s and father’s low educational attainment; 4) financial difficulties; 5) relationship with partner, comprising a) status, b) lack of affection, c) cruelty, d) lack of support; 6) family, comprising a) size, b) child in care, not with natural mother, on at-risk register; 7) social network, comprising a) lack of emotional support, b) lack of practical support; 8) substance abuse; 9) crime, comprising a) being in trouble with the police and b) convictions; and 10) psychopathology of the mother (anxiety, depression or suicide attempts). Each of the 18 items is assigned a value of 1 if an adversity is present and 0 if it is not present hence, the FAI has a theoretical range of 0 to 18. FAI scores are calculated where more than half of the items are valid, and non-adversity is assumed for any missing data hence, FAI scores are conservative. Several components of the FAI (age at first pregnancy, overcrowding, family size, rented housing, and maternal anxiety) were previously shown to be associated with wheezing phenotypes [14].

Statistical methods

Associations of pet ownership with episodes of wheezing at ages 6, 18, 32, 42, and 81 months and with lung function (FEV1 and FVC) were investigated using logistic and linear regression models, respectively, adjusted for sex of child, maternal history of asthma or allergy, maternal smoking during pregnancy, and family adversity index. FEV1 and FVC were quantified as units of standard deviations (z-scores). The relationship of pet ownership with wheeze over all five time-points was investigated using random effects logit regression models. We analysed ownership of fish, turtles and tortoises in relation to wheezing episodes (as a negative control), but we could not categorize ownership as a 4-level categorical variable because fish/turtle/tortoise ownership was recorded only from age 2 years onwards. Associations of pet ownership with wheezing phenotypes were estimated using multinomial logistic regression models weighted by the probability for each individual of belonging to each phenotype. These probabilities were estimated previously and referred to as the posterior probabilities [12]. According to this method, each child contributes a line of data corresponding to each phenotype for which the child has a non-zero posterior probability. For example, a child might have posterior probability 0.9 of persistent wheeze, 0.1 of transient early wheeze and zero for all other phenotypes. In the regression analyses, this child would contribute two lines of data, the first for persistent wheeze with weight 0.9 and the second for transient early wheeze with weight 0.1. Adjusted relative risk ratios (also known as multinomial odds ratios) were derived in relation to the never/infrequent wheezing phenotype (reference group). Heterogeneity p-values comparing estimated effects across wheezing phenotypes were calculated using Chi-squared tests. Models which used a specific pet type as exposure were not adjusted for the presence of other pets. Pet ownership status over time was modelled by means of the 4-level categorical pet ownership variable, which was coded to indicate non-ownership (i.e. never owned, at any time point), ‘continuous’ ownership (owned at any time point before age 33 months and at any time point thereafter), and ‘discontinuous’ ownership, comprising: pet ‘acquired’ after age 3 years (not previously owned), or pet owned up to age 3 but not afterwards. Estimates for the two ‘discontinuous’ ownership levels give some indication as to whether ‘early’ or ‘late’ ownership has a similar effect on outcomes compared with non-ownership or ‘continuous’ ownership. All analyses were performed using Stata (StataCorp, College Station, TX, USA).


Of 13,978 children in ALSPAC, 4,706 children (33.7%) had complete data on wheezing, pet ownership and confounders (maternal history of allergy/asthma, maternal smoking during pregnancy and family adversity index). The distributions of exposures and outcomes in the complete data group are summarized in Table 1. Our analysis of lung function was based on 4,177 children (29.9%), and our analyses of pet ownership during pregnancy in relation to wheeze at age 6 months, wheezing phenotypes and lung function were based on 8,661 (62.0%), 5,735 (41.0%) and 5,278 (37.8%) children, respectively. Children with complete data were similar to children with missing data, except that children with complete data were less likely to have had wheeze at age 6 months, had mothers who were less likely to have smoked during pregnancy, and lived in households which had lower levels of adversity and which were less likely to own pets (S1 Table). As reported previously, maternal smoking during pregnancy and family adversity were strongly positively associated with pet ownership, and pet ownership tended to be less common among mothers who reported a history of allergy [7].

Table 1. Outcomes and exposures in children with complete data (N = 4,706).

Pet ownership and wheezing

Ownership of any pet was associated with 13% higher odds of wheezing at age 6–8 months (odds ratio (OR) = 1.13; 95% CI 1.02–1.25) but there was no association at any of the later time-points and no overall association. Cat ownership was associated with lower odds of wheezing at ages 18 and 42 months with an overall 6% lower odds of wheezing (OR = 0.94; 95% CI 0.89–0.99) (Table 2, S2 Table). Conversely, owning a rabbit or rodent increased the overall odds of wheezing by 21% (OR = 1.21; 95% CI 1.12–1.31) and 11% (OR = 1.11; 95% CI 1.02–1.21), respectively, with the strongest associations evident during infancy. As expected, ownership of fish, turtles and tortoises was not associated with occurrence of wheezing.

Table 2. Associations of pet ownership at different time-points during childhood with concurrent wheezing episodes.


Pet ownership was not associated with wheezing phenotypes, with the exception of positive associations of rabbit and rodent ownership with persistent wheeze (Table 3, S3 Table). There was no overall heterogeneity in associations across the different phenotypes for any pet type (all P>0.2). Point estimates suggested opposing effects of pet ownership on intermediate onset (inverse association) versus persistent wheeze (positive association), and there was statistical evidence of heterogeneity between these two phenotypes for continuous ownership (before and after age 3 years) of any pet type: intermediate onset OR = 0.67 (95% CI 0.42–1.06); persistent wheeze OR = 1.26 (95% CI 0.88–1.80); heterogeneity P = 0.03.

Table 3. Associations of pet ownership during childhood with wheezing phenotypes.


Dog, rabbit and bird ownership during pregnancy were associated with higher odds of wheeze at age 6 months but there were no associations of pet ownership during pregnancy with any of the wheezing phenotypes (Table 4, S2 Table). Of the 57.5% (2,708/4,706) of households recorded as owning any pet type during pregnancy, the majority (87.9% (2,381/2,708)) also reported owning a pet when the child was 6 months old. However, there was some variation by pet type: of households recorded during pregnancy as owning a cat (32.5%), dog (21.4%), rabbit (7.7%), rodent (5.1%) or bird (6.5%), the proportions owning these types of pets when the child was 6 months old were 87.8% (cats), 86.1% (dogs), 68.0% (rabbits), 53.1% (rodents), and 66.7% (birds). Acquisition of a pet in the 6 months after the birth of the child by households which had previously not owned that pet type was uncommon: cats (1.5% (46/3,178)), dogs (1.0% (38/3,701)), rabbits (2.7% (118/4,344)), rodents (2.0% (89/4,467)), and birds (1.3% (56/4,400)).

Table 4. Associations of pet ownership during pregnancy with wheeze at 6–8 months and with wheezing phenotypes.

Pet ownership and lung function

Pet ownership was not associated with lung function at age 8 years (Table 5), with the exception of positive associations of rodent and bird ownership with better lung function. For rodent ownership (comparing ever owned versus never owned), the mean difference in FEV1 z-score was 0.072 (95% CI 0.008 to 0.136, P = 0.03), and the mean difference in FVC z-score was 0.065 (95% CI 0.003 to 0.127, P = 0.04); for bird ownership, the mean difference in FEV1 z-score was 0.105 (95% CI 0.014 to 0.195, P = 0.02). There were no consistent patterns in the sign of the point estimate (greater or less than zero) for the mean differences in FEV1 and FVC across levels of pet ownership or between pet types.

Table 5. Associations of pet ownership with lung function at age 8 years (N = 4,177).


Rabbit and rodent ownership in this birth cohort was associated with an increased risk, and cat ownership with a slightly reduced risk, of episodes of wheezing during early childhood. The positive associations of rabbit and rodent ownership were most evident during infancy, and also manifested as an increased risk of a ‘persistent wheeze’ phenotype. Cat ownership was not associated with any of the six wheezing phenotypes. We found weak evidence of apparently paradoxical positive associations of rodent and bird ownership with better lung function (FEV1 and FVC) at age 8 years, but these are most plausibly ascribed to chance. Dog, rabbit and bird ownership during pregnancy was positively associated with wheezing at age 6 months. These associations may simply reflect the fact that the majority of these households also owned these pet types at age 6 months, rather than indicating specific in utero effects.

Strengths and limitations

ALSPAC is a well-characterized birth cohort which has provided data for several studies into in utero and early childhood factors in relation to childhood asthma, wheezing and atopy [7,14,1923]. A key strength of our study was the availability of exposure measures derived from identical questionnaire items for specific pet types at multiple time-points, from pregnancy through to age 7 years, plus data for potential confounders. The main limitation of our study, as with any birth cohort, relates to losses to follow-up; specifically, the possible effects of higher rates of attrition among children from less affluent families [15]. Given that such children were more likely to be exposed to household pets and to experience wheezing, we would tend to under-estimate associations between pet ownership and wheezing. However, we found that crude associations were affected little by adjustment for family adversity or potential confounding factors such as smoking during pregnancy, and the results of complete-data analyses were similar to results obtained using the maximum amount of available data. This suggests that our results would not be substantially biased by higher losses to follow-up in the lower social strata.

We found that the inclusion of potential confounders made little or no difference to our point estimates, but we cannot discount residual confounding due to unmeasured confounders, for example, number of siblings, time spent outdoors, physical activity, etc. Our dataset did not include factors which might mediate some of our observed associations, in particular whether pets were kept indoors or outdoors, type of dog owned (e.g. moulting versus non-moulting), and the frequency and type of contact between children and pets. Future research could investigate dose-response effects in terms of the number and variety of pets owned. We used ownership at any point before age 3 years (including during pregnancy) and at any point thereafter as a pragmatic proxy for ‘continuous’ ownership, rather than strictly identifying households which had uninterrupted pet ownership. We used wheezing phenotypes and pet exposure variables which had been defined for the purpose of previously published analyses—a more sophisticated de novo longitudinal analysis using, for example, structural equation modelling, could be used to better elucidate causal associations. This would also minimize the risk of Type 1 error which, because of the large number of permutations of exposure and outcomes, requires us to exercise extra caution in interpreting our results.

Our findings in the context of other studies

Systematic reviews have reported conflicting evidence, from a wide range of study designs, for the effects of early life exposure to household pets (mainly cats and dogs) and the development of asthma [2426]. To our knowledge, no other studies have investigated ownership of a wide range of pet types in relation to wheeze at multiple time-points throughout childhood. Brussee et al reported inconclusive evidence for (generally positive) associations of cat and dog allergen exposure at 3 months of age with ‘persistent’ and ‘early transient’ wheeze phenotypes, but children were followed up only to age 4 years (and there were few children in the ‘late onset’ phenotype) [27]. Sandin et al reported a positive association of dog ownership during the first year of life with a ‘transient’ wheeze phenotype and an inverse association with a ‘late onset’ phenotype, but these phenotypes were also defined for children aged 4 years [28]. In a cohort of children predisposed to asthma or atopy (as indicated by parental history), exposure to cat allergen and dog ownership were inversely associated with repeated wheezing episodes during the first 4–5 years of life [29]. This overall inverse association obscured a positive association, which tended to increase year-on-year, among children whose mothers had a history of asthma [30]. Perzanowski et al reported strong positive associations between cat ownership and sensitization to cat allergen by age 2 years, and between sensitization and wheeze at ages 3 and 5 years [31]. However, there was an overall inverse association between cat ownership and risk of wheeze at age 5 years, which was strongest among children who were not sensitized and among children whose mothers did not have a history of asthma. Remes et al found an inverse association between dog exposure and onset of wheezing up to age 11 years [32]. This was evident only among children who had a parent with a history of asthma, and there were no associations between cat exposure and wheezing.

Our study contributes an overall inverse association of cat ownership with repeated episodes of wheezing up to the age of 7 years (and no effect of dog ownership) to a diversity of findings for cats and dogs. This diversity can probably be attributed to differences in study design and to variation in factors such as genetic susceptibility (parental history) and background levels of allergen (related to prevalence of pet ownership), and in other environmental and lifestyle factors. Our findings of apparent ‘protective’ effects of cat ownership and ‘harmful’ effects of rabbit and rodent ownership on episodes of wheezing are consistent with our earlier findings from this cohort of children [7]. Specifically, we reported that continuous cat ownership (before and after age 3 years) was associated with 32% (OR = 0.68; 95% CI 0.49–0.95) lower odds of atopic asthma, and continuous ownership of rabbits and rodents with 61% and 86% higher odds, respectively, of non-atopic asthma (OR = 1.61; 95% CI 1.04–2.51 and OR = 1.86; 95% CI 1.15–3.01).

That our other earlier findings of inverse associations of pet ownership with atopic asthma and (weak) positive associations with non-atopic asthma were not clearly evident in our analysis of wheezing phenotypes reflects the non-specific nature of wheeze as a symptom of atopic versus non-atopic asthma, both of which were very strongly associated with the intermediate onset and persistent wheezing phenotypes. However, pet ownership tended to be associated with lower risk of the ‘intermediate onset’ wheezing phenotype, which had the strongest association with atopy compared with the never/infrequent phenotype [12]. Similarly, we found evidence of heterogeneity in the effects of ownership of any pet type on ‘intermediate onset’ wheezing (reduced risk) versus ‘persistent’ wheeze (increased risk) which echoes our earlier finding of heterogeneity in the effects of ownership of any pet type on atopic asthma (reduced risk) versus non-atopic asthma (increased risk) [7], and which appears consistent with the intermediate onset wheezing phenotype being strongly associated with sensitization to common allergens at age 4 years (in two birth cohorts) [33]. In the present study we interpret this apparent heterogeneity with some caution, given the overall absence of heterogeneity across the phenotypes, and the number of possible pairwise tests.

Implications for clinical practice and future research

Our data point to differential effects across pet types, but do not indicate what aspect(s) of pets and pet ownership may be associated with an increased risk versus a protective effect. Pet ownership practices vary by species, and proximity and frequency of pet contact could be important factors, along with factors such as types of bedding used (hay, sawdust, etc). Future research could focus on environmental characteristics associated with different types of pet; fuller details about the domestic husbandry of small mammals such as pet rabbits and rodents will be needed to pinpoint specific risks. Endotoxins, allergens, and other irritants in the home environment might give clues to the causative exposure in much same way as farming studies identified endotoxin as protective exposures for allergy [3436]. Interactions of environmental characteristics with genetic variation also warrant exploration in relation to exposure to household pets [4,37,38].


We found ‘protective’ effects of cat ownership and ‘harmful’ effects of rabbit and rodent ownership on wheezing which are consistent with earlier findings from this cohort of children. Parents, or prospective parents, may wish to consider these effects when deciding whether or not to own pets, but whether exposure to pets has a causal effect on the development of wheeze-related disease or whether exposure simply triggers wheezing remains to be elucidated.

Supporting Information

S1 Table. Characteristics of children in our analysis compared with children who had missing data on wheezing and pet ownership.


S2 Table. Frequency distributions for pet ownership at different time-points and concurrent wheezing episodes.


S3 Table. Distributions of wheezing phenotypes by level of pet ownership.



We are extremely grateful to all the families who took part in this study, the midwives for their help in recruiting them, and the whole ALSPAC team, which includes interviewers, computer and laboratory technicians, clerical workers, research scientists, volunteers, managers, receptionists and nurses.

Author Contributions

Conceived and designed the experiments: AJH JACS ESP JM. Analyzed the data: SMC JACS. Contributed reagents/materials/analysis tools: RG CW. Wrote the paper: AJH JACS ESP JM SMC RG CW.


  1. 1. Sennhauser FH, Braun-Fahrlander C, Wildhaber JH (2005) The burden of asthma in children: a European perspective. Paediatr Respir Rev 6: 2–7. pmid:15698807
  2. 2. Wildhaber J, Carroll WD, Brand PL (2012) Global impact of asthma on children and adolescents' daily lives: the room to breathe survey. Pediatr Pulmonol 47: 346–357. pmid:22028276
  3. 3. Peters JL, Boynton-Jarrett R, Sandel M (2013) Prenatal environmental factors influencing IgE levels, atopy and early asthma. Curr Opin Allergy Clin Immunol 13: 187–192. pmid:23385288
  4. 4. Blekic M, Kljaic Bukvic B, Aberle N, Marinho S, Hankinson J, Custovic A et al. (2013) 17q12-21 and asthma: interactions with early-life environmental exposures. Ann Allergy Asthma Immunol 110: 347–353. pmid:23622005
  5. 5. Anderson HR, Gupta R, Strachan DP, Limb ES (2007) 50 years of asthma: UK trends from 1955 to 2004. Thorax 62: 85–90. pmid:17189533
  6. 6. Westgarth C, Heron J, Ness AR, Bundred P, Gaskell RM, Coyne KP et al. (2010) Family pet ownership during childhood: findings from a UK birth cohort and implications for public health research. Int J Environ Res Public Health 7: 3704–3729. pmid:21139856
  7. 7. Collin SM, Granell R, Westgarth C, Murray J, Paul E, Sterne JA et al. (2014) Pet ownership is associated with increased risk of non-atopic asthma and reduced risk of atopy in childhood: findings from a UK birth cohort. Clin Exp Allergy 45: 200–210.
  8. 8. Apelberg BJ, Aoki Y, Jaakkola JJ (2001) Systematic review: Exposure to pets and risk of asthma and asthma-like symptoms. J Allergy Clin Immunol 107: 455–460. pmid:11240945
  9. 9. Takkouche B, Gonzalez-Barcala FJ, Etminan M, Fitzgerald M (2008) Exposure to furry pets and the risk of asthma and allergic rhinitis: a meta-analysis. Allergy 63: 857–864. pmid:18588551
  10. 10. Lodrup Carlsen KC, Roll S, Carlsen KH, Mowinckel P, Wijga AH, Brunekreef B et al. (2012) Does pet ownership in infancy lead to asthma or allergy at school age? Pooled analysis of individual participant data from 11 European birth cohorts. PLoS One 7: e43214. pmid:22952649
  11. 11. Lotvall J, Akdis CA, Bacharier LB, Bjermer L, Casale TB, Custovic A et al. (2011) Asthma endotypes: a new approach to classification of disease entities within the asthma syndrome. J Allergy Clin Immunol 127: 355–360. pmid:21281866
  12. 12. Henderson J, Granell R, Heron J, Sherriff A, Simpson A, Woodcock A et al. (2008) Associations of wheezing phenotypes in the first 6 years of life with atopy, lung function and airway responsiveness in mid-childhood. Thorax 63: 974–980. pmid:18678704
  13. 13. Belgrave DC, Simpson A, Semic-Jusufagic A, Murray CS, Buchan I, Pickles A et al. (2013) Joint modeling of parentally reported and physician-confirmed wheeze identifies children with persistent troublesome wheezing. J Allergy Clin Immunol 132: 575–583. pmid:23906378
  14. 14. Granell R, Sterne JA, Henderson J (2012) Associations of different phenotypes of wheezing illness in early childhood with environmental variables implicated in the aetiology of asthma. PLoS One 7: e48359. pmid:23118993
  15. 15. Boyd A, Golding J, Macleod J, Lawlor DA, Fraser A, Henderson J et al. (2012) Cohort Profile: The 'Children of the 90s'—the index offspring of the Avon Longitudinal Study of Parents and Children. Int J Epidemiol 42: 111–127. pmid:22507743
  16. 16. American Thoracic Society (1995) Standardization of Spirometry, 1994 Update. Am J RespirCrit Care Med 152: 1107–1136.
  17. 17. Chinn S, Rona RJ (1992) Height and age adjustment for cross sectional studies of lung function in children aged 6–11 years. Thorax 47: 707–714. pmid:1440464
  18. 18. Svanes C, Zock JP, Anto J, Dharmage S, Norback D, Wjst M et al. (2006) Do asthma and allergy influence subsequent pet keeping? An analysis of childhood and adulthood. J Allergy Clin Immunol 118: 691–698. pmid:16950289
  19. 19. Callard RE, Hamvas R, Chatterton C, Blanco C, Pembrey M, Jones R et al. (2002) An interaction between the IL-4Ralpha gene and infection is associated with atopic eczema in young children. Clin Exp Allergy 32: 990–993. pmid:12100043
  20. 20. Cookson H, Granell R, Joinson C, Ben-Shlomo Y, Henderson AJ (2009) Mothers' anxiety during pregnancy is associated with asthma in their children. J Allergy Clin Immunol 123: 847–853. pmid:19348924
  21. 21. Shaheen SO, Newson RB, Henderson AJ, Emmett PM, Sherriff A, Cooke M et al. (2004) Umbilical cord trace elements and minerals and risk of early childhood wheezing and eczema. Eur Respir J 24: 292–297. pmid:15332400
  22. 22. Shaheen SO, Newson RB, Henderson AJ, Headley JE, Stratton FD, Jones RW et al. (2005) Prenatal paracetamol exposure and risk of asthma and elevated immunoglobulin E in childhood. Clin Exp Allergy 35: 18–25. pmid:15649261
  23. 23. Shaheen SO, Northstone K, Newson RB, Emmett PM, Sherriff A, Henderson AJ (2009) Dietary patterns in pregnancy and respiratory and atopic outcomes in childhood. Thorax 64: 411–417. pmid:19213776
  24. 24. Dick S, Friend A, Dynes K, AlKandari F, Doust E, Cowie H et al. (2014) A systematic review of associations between environmental exposures and development of asthma in children aged up to 9 years. BMJ Open 4: e006554. pmid:25421340
  25. 25. Chen CM, Tischer C, Schnappinger M, Heinrich J (2010) The role of cats and dogs in asthma and allergy—a systematic review. Int J Hyg Environ Health 213: 1–31. pmid:20053584
  26. 26. Lodge CJ, Allen KJ, Lowe AJ, Hill DJ, Hosking CS, Abramson MJ et al. (2012) Perinatal cat and dog exposure and the risk of asthma and allergy in the urban environment: a systematic review of longitudinal studies. Clin Dev Immunol 2012: 176484. pmid:22235226
  27. 27. Brussee JE, Smit HA, van Strien RT, Corver K, Kerkhof M, Wijga AH et al. (2005) Allergen exposure in infancy and the development of sensitization, wheeze, and asthma at 4 years. J Allergy Clin Immunol 115: 946–952. pmid:15867850
  28. 28. Sandin A, Bjorksten B, Braback L (2004) Development of atopy and wheezing symptoms in relation to heredity and early pet keeping in a Swedish birth cohort. Pediatr Allergy Immunol 15: 316–322. pmid:15305940
  29. 29. Litonjua AA, Milton DK, Celedon JC, Ryan L, Weiss ST, Gold DR (2002) A longitudinal analysis of wheezing in young children: the independent effects of early life exposure to house dust endotoxin, allergens, and pets. J Allergy Clin Immunol 110: 736–742. pmid:12417882
  30. 30. Celedon JC, Litonjua AA, Ryan L, Platts-Mills T, Weiss ST, Gold DR (2002) Exposure to cat allergen, maternal history of asthma, and wheezing in first 5 years of life. Lancet 360: 781–782. pmid:12241839
  31. 31. Perzanowski MS, Chew GL, Divjan A, Johnson A, Goldstein IF, Garfinkel RS et al. (2008) Cat ownership is a risk factor for the development of anti-cat IgE but not current wheeze at age 5 years in an inner-city cohort. J Allergy Clin Immunol 121: 1047–1052. pmid:18395554
  32. 32. Remes ST, Castro-Rodriguez JA, Holberg CJ, Martinez FD, Wright AL (2001) Dog exposure in infancy decreases the subsequent risk of frequent wheeze but not of atopy. J Allergy Clin Immunol 108: 509–515. pmid:11590373
  33. 33. Savenije OE, Granell R, Caudri D, Koppelman GH, Smit HA, Wijga A et al. (2011) Comparison of childhood wheezing phenotypes in 2 birth cohorts: ALSPAC and PIAMA. J Allergy Clin Immunol 127: 1505–1512. pmid:21411131
  34. 34. Heinrich J, Gehring U, Douwes J, Koch A, Fahlbusch B, Bischof W et al. (2001) Pets and vermin are associated with high endotoxin levels in house dust. Clin Exp Allergy 31: 1839–1845. pmid:11737034
  35. 35. Illi S, Depner M, Genuneit J, Horak E, Loss G, Strunz-Lehner C et al. (2012) Protection from childhood asthma and allergy in Alpine farm environments-the GABRIEL Advanced Studies. J Allergy Clin Immunol 129: 1470–1477. pmid:22534534
  36. 36. Liu AH (2004) Something old, something new: indoor endotoxin, allergens and asthma. Paediatr Respir Rev 5 Suppl A: S65–71.
  37. 37. Ege MJ, Strachan DP, Cookson WO, Moffatt MF, Gut I, Lathrop M et al. (2011) Gene-environment interaction for childhood asthma and exposure to farming in Central Europe. J Allergy Clin Immunol 127: 138–144. pmid:21211648
  38. 38. Kauffmann F, Demenais F (2012) Gene-environment interactions in asthma and allergic diseases: challenges and perspectives. J Allergy Clin Immunol 130: 1229–1240. pmid:23195523