Division of Pulmonary, Allergy and Critical Care of Medicine, Department of Medicine, College of Physicians and Surgeons, Columbia University, PH8E-101, 630 W. 168th Street, New York, NY 10032, United States.
Mailman School of Public Health, Department of Environmental Health Sciences, Columbia University, 722 W. 168 Street, New York, NY 10032, United States.
Environ Res. 2014 Jan;128:35-41. doi: 10.1016/j.envres.2013.12.002. Epub 2013 Dec 27.
Exposure to traffic-related air pollutants, including polycyclic aromatic hydrocarbons (PAHs) from traffic emissions and other combustion sources, and childhood obesity, have been implicated as risk factors for developing asthma. However, the interaction between these two on asthma among young urban children has not been studied previously.
Exposure to early childhood PAHs was measured by two week residential indoor monitoring at age 5-6 years in the Columbia Center for Children's Environmental Health birth cohort (n=311). Semivolatile [e.g., methylphenanthrenes] and nonvolatile [e.g., benzo(a)pyrene] PAHs were monitored. Obesity at age 5 was defined as a body mass index (BMI) greater than or equal to the 95th percentile of the year 2000 age- and sex-specific growth charts (Center for Disease Control). Current asthma and recent wheeze at ages 5 and 7 were determined by validated questionnaires. Data were analyzed using a modified Poisson regression in generalized estimating equations (GEE) to estimate relative risks (RR), after adjusting for potential covariates.
Neither PAH concentrations or obesity had a main effect on asthma or recent wheeze. In models stratified by presence/absence of obesity, a significant positive association was observed between an interquartile range (IQR) increase in natural log-transformed 1-methylphenanthrene (RR [95% CI]: 2.62 [1.17-5.88] with IQRln=0.76), and 9-methylphenanthrene (2.92 [1.09-7.82] with IQRln=0.73) concentrations and asthma in obese children (n=63). No association in non-obese (n=248) children was observed at age 5 (Pinteraction<0.03). Similar associations were observed for 3-methylphenanthrene, 9-methylphenanthrene, and 3,6-dimethylphenanthrene at age 7.
Obese young children may be more likely to develop asthma in association with greater exposure to PAHs, and methylphenanthrenes in particular, than non-obese children.
交通相关空气污染物(包括交通排放和其他燃烧源产生的多环芳烃[PAHs])和儿童肥胖已被认为是引发哮喘的风险因素。然而,此前尚未研究这两种因素对城市幼儿哮喘的相互作用。
在哥伦比亚儿童环境健康出生队列研究(n=311)中,在 5-6 岁时通过两周的家庭室内监测来测量儿童早期接触 PAHs 的情况。监测半挥发性[例如,甲基菲]和非挥发性[例如,苯并[a]芘]PAHs。5 岁时肥胖的定义为体质指数(BMI)大于或等于 2000 年年龄和性别特定生长图表的第 95 百分位数(疾病控制中心)。5 岁和 7 岁时通过验证问卷确定当前哮喘和近期喘息。使用广义估计方程(GEE)中的修正泊松回归分析数据,以估计相对风险(RR),在调整潜在协变量后进行。
PAH 浓度或肥胖均对哮喘或近期喘息无主要影响。在按肥胖存在/不存在分层的模型中,观察到自然对数变换的 1-甲基菲(RR [95%CI]:2.62 [1.17-5.88]与 IQRln=0.76)和 9-甲基菲(RR [95%CI]:2.92 [1.09-7.82]与 IQRln=0.73)浓度与肥胖儿童(n=63)哮喘之间存在显著正相关。在非肥胖儿童(n=248)中未观察到与年龄 5 相关的关联(Pinteraction<0.03)。在年龄 7 时也观察到了类似的关联,涉及 3-甲基菲、9-甲基菲和 3,6-二甲基菲。
与非肥胖儿童相比,肥胖的幼儿可能更容易因接触更多的 PAHs(特别是甲基菲)而患上哮喘。