Global Health Institute, School of Medicine, Duke University, Durham, NC, USA; Children's Environmental Health Initiative, University of Illinois Chicago, Chicago, IL, USA.
Children's Environmental Health Initiative, University of Illinois Chicago, Chicago, IL, USA.
Environ Res. 2024 Jan 1;240(Pt 1):117509. doi: 10.1016/j.envres.2023.117509. Epub 2023 Oct 26.
Previous studies have observed associations between birth weight and prenatal air pollution exposure, but there is not consensus on timing of critical windows of susceptibility.
We estimated the difference in birth weight among preterm, early term and full term births associated with weekly exposure to PM and NO throughout gestation.
We included all singleton live births in the Lower Peninsula of Michigan (United States) between 2007 and 2012 occurring at or after 32 weeks gestational age (n = 497,897). Weekly ambient PM and NO concentrations were estimated at maternal residences using 1-km gridded data from ensemble-based models. We utilized a distributed lag nonlinear model to estimate the difference in birth weight associated with weekly exposures from the last menstrual period (week 0) through 31 weeks gestation for preterm births; through 36 weeks gestation for early term births; and through 38 weeks gestation for full term births.
In single-pollutant models, a 5 μg/m increase in PM exposure was associated with a reduction in birth weight among preterm births (-37.1 g [95% confidence interval [CI]: 60.8 g, -13.5 g]); early term births (-13.5 g [95% CI: 26.2 g, -0.67 g]); and full term births (-8.23 g [95% CI: 15.8 g, -0.68 g])]. In single-pollutant models, a 10 ppb increase in NO exposure was associated with a -11.7 g (95% CI: 14.46 g, -8.92 g) decrement in birth weight among full term births only. In models co-adjusted for PM and NO, PM exposure was associated with reduced birth weight among preterm births (-36.9 g [95% CI: 61.9 g, -11.8 g]) and NO exposure was associated with reduced birth weight among full term births (-11.8 g [95% CI: 14.7 g, -8.94 g]). The largest decrements in birth weight were associated with PM exposure between approximately 10 and 26 weeks of pregnancy; for NO exposure, the largest decrements in birth weight in full term births were associated with exposure between weeks 6-18.
We observed the largest and most persistent adverse associations between PM exposure and birth weight in preterm infants, and between NO exposure and birth weight in full term infants. Exposure during the first half of pregnancy had a greater impact on birthweight.
先前的研究已经观察到出生体重与产前空气污染暴露之间的关联,但对于易感窗口期的时间仍没有共识。
我们估计了整个孕期每周暴露于 PM 和 NO 与早产儿、早期足月产和足月产之间的出生体重差异。
我们纳入了 2007 年至 2012 年期间在美国密歇根州下半岛发生的 32 周及以上胎龄的所有单胎活产儿(n=497897)。使用基于集合的模型的 1 公里网格化数据,在母体住所估计每周的环境 PM 和 NO 浓度。我们利用分布式滞后非线性模型,估计从末次月经(第 0 周)到早产的 31 周;早期足月产的 36 周;以及足月产的 38 周的每周暴露与出生体重相关的差异。
在单污染物模型中,PM 暴露增加 5μg/m 与早产儿出生体重下降相关(-37.1g[95%置信区间(CI):60.8g,-13.5g]);早期足月产(-13.5g[95%CI:26.2g,-0.67g]);以及足月产(-8.23g[95%CI:15.8g,-0.68g])]。在单污染物模型中,NO 暴露增加 10ppb 与足月产出生体重下降 11.7g(95%CI:14.46g,-8.92g)相关。在同时调整 PM 和 NO 的模型中,PM 暴露与早产儿出生体重下降相关(-36.9g[95%CI:61.9g,-11.8g]),而 NO 暴露与足月产出生体重下降相关(-11.8g[95%CI:14.7g,-8.94g])。与出生体重下降相关的最大降幅与 PM 暴露发生在妊娠约 10 至 26 周之间;对于 NO 暴露,足月产中与出生体重下降相关的最大降幅与妊娠 6-18 周之间的暴露有关。
我们观察到 PM 暴露与早产儿出生体重之间以及 NO 暴露与足月产出生体重之间最大且最持久的不良关联。妊娠前半段的暴露对出生体重的影响更大。