Yiin L M, Rhoads G G, Lioy P J
Environmental and Occupational Health Sciences Institute, Department of Environmental Sciences, Rutgers, The State University of New Jersey, Piscataway, New Jersey, USA.
Environ Health Perspect. 2000 Feb;108(2):177-82. doi: 10.1289/ehp.00108177.
We conducted a study to examine seasonal changes in residential dust lead content and its relationship to blood lead in preschool children. We collected blood and dust samples (floors, windowsills, and carpets) to assess lead exposure. The geometric mean blood lead concentrations are 10.77 and 7.66 microg/dL for the defined hot and cold periods, respectively (p < 0.05). Lead loading (milligrams per square meter) is the measure derived from floor and windowsill wipe samples that is most correlated with blood lead concentration, whereas lead concentration (micrograms per gram) is the best variable derived from carpet vacuum samples. The variation of dust lead levels for these three dust variables (floor lead loading, windowsill lead loading, and carpet lead concentration) are consistent with the variation of blood lead levels, showing the highest levels in the hottest months of the year, June, July, and August. The regression analysis, including the three representative dust variables in the equations to predict blood lead concentration, suggests that the seasonality of blood lead levels in children is related to the seasonal distributions of dust lead in the home. In addition, the outdoor activity patterns indicate that children are likely to contact high leaded street dust or soil during longer outdoor play periods in summer. Consequently, our results show that children appear to receive the highest dust lead exposure indoors and outdoors during the summer, when they have the highest blood lead levels. We conclude that at least some of the seasonal variation in blood lead levels in children is probably due to increased exposure to lead in dust and soil.
我们开展了一项研究,以调查住宅灰尘中铅含量的季节性变化及其与学龄前儿童血铅的关系。我们采集了血液和灰尘样本(地板、窗台和地毯)来评估铅暴露情况。在规定的炎热期和寒冷期,几何平均血铅浓度分别为10.77和7.66微克/分升(p<0.05)。铅负荷(每平方米毫克数)是根据地板和窗台擦拭样本得出的与血铅浓度相关性最强的指标,而铅浓度(每克微克数)是根据地毯吸尘样本得出的最佳变量。这三个灰尘变量(地板铅负荷、窗台铅负荷和地毯铅浓度)的灰尘铅水平变化与血铅水平变化一致,在一年中最热的月份,即6月、7月和8月呈现最高水平。回归分析在预测血铅浓度的方程中纳入了这三个具有代表性的灰尘变量,结果表明儿童血铅水平的季节性与家中灰尘铅的季节性分布有关。此外,户外活动模式表明,在夏季较长的户外玩耍期间,儿童可能会接触到含铅量高的街道灰尘或土壤。因此,我们的结果表明,儿童在夏季血铅水平最高时,在室内和室外似乎都受到了最高的灰尘铅暴露。我们得出结论,儿童血铅水平至少部分季节性变化可能是由于接触灰尘和土壤中的铅增加所致。