Li Wenchao, Chien Jiayang, Cohen Joel M
Gradient, One Beacon St, 17th Floor, Boston, MA 02108, United States.
J Occup Health. 2024 Jan 4;67(1). doi: 10.1093/joccuh/uiae073.
To date there has been little observational evidence on the relationship between air lead and blood lead at relatively low workplace air lead concentrations. This study sought to improve upon prior studies methodologically and aimed to examine this relationship in a modern workplace environment.
Personal measurements of air lead and blood lead concentrations were collected in a modern lead-acid battery manufacturing facility in the United States. A total of 236 workers and their 2221 air-blood lead measurement pairs, collected between 2001 and 2021, were included in the statistical analysis. The association between air lead and blood lead was examined using linear mixed-effects models to account for data correlation. Potential confounders adjusted for included age, sex, job department, time trend, tenure, and seasonality.
The workers were mostly (83%) male and on average 29.75 years of age at the first included measurement. Their air lead concentrations ranged from 1 to 50 (arithmetic mean 16.85) μg/m3; blood lead concentrations ranged from 2 to 35 (arithmetic mean 15.47) μg/dL. After adjusting for potential confounders, a 1 μg/m3 increment in air lead was associated with a 0.025 (95% CI, 0.005-0.045; marginal, semi-partial ${R}^2$ = 0.002) μg/dL higher blood lead.
The relationship between air lead and blood lead at relatively low workplace air lead concentrations over a long employment period may be very weak, but this needs to be further investigated in future observational studies with quantified lead exposures from noninhalation routes and nonoccupational sources.
迄今为止,关于工作场所空气中铅浓度相对较低时空气铅与血铅之间的关系,几乎没有观察性证据。本研究试图在方法上改进先前的研究,并旨在在现代工作场所环境中检验这种关系。
在美国一家现代铅酸电池制造工厂收集了空气铅和血铅浓度的个人测量数据。在2001年至2021年期间收集的总共236名工人及其2221对空气-血铅测量数据纳入了统计分析。使用线性混合效应模型来检验空气铅与血铅之间的关联,以考虑数据相关性。调整的潜在混杂因素包括年龄、性别、工作部门、时间趋势、任期和季节性。
这些工人大多(83%)为男性,首次纳入测量时平均年龄为29.75岁。他们的空气铅浓度范围为1至50(算术平均值16.85)μg/m³;血铅浓度范围为2至35(算术平均值15.47)μg/dL。在调整潜在混杂因素后,空气铅每增加1μg/m³,血铅就会升高0.025(95%CI,0.005 - 0.045;边际,半偏${R}^2$ = 0.002)μg/dL。
在较长的就业期间,工作场所空气中铅浓度相对较低时,空气铅与血铅之间的关系可能非常微弱,但这需要在未来的观察性研究中进一步调查,以量化来自非吸入途径和非职业来源的铅暴露情况。