Gaitens Joanna M, Dixon Sherry L, Jacobs David E, Nagaraja Jyothi, Strauss Warren, Wilson Jonathan W, Ashley Peter J
Healthy Housing Solutions, Inc., Columbia, Maryland 21044, USA.
Environ Health Perspect. 2009 Mar;117(3):461-7. doi: 10.1289/ehp.11917. Epub 2008 Nov 14.
Lead-contaminated house dust is a major source of lead exposure for children in the United States. In 1999-2004, the National Health and Nutrition Examination Survey (NHANES) collected dust lead (PbD) loading samples from the homes of children 12-60 months of age.
In this study we aimed to compare national PbD levels with existing health-based standards and to identify housing and demographic factors associated with floor and windowsill PbD.
We used NHANES PbD data (n=2,065 from floors and n=1,618 from windowsills) and covariates to construct linear and logistic regression models.
The population-weighted geometric mean floor and windowsill PbD were 0.5 microg/ft2 [geometric standard error (GSE)=1.0] and 7.6 microg/ft2 (GSE=1.0), respectively. Only 0.16% of the floors and 4.0% of the sills had PbD at or above current federal standards of 40 and 250 microg/ft2, respectively. Income, race/ethnicity, floor surface/condition, windowsill PbD, year of construction, recent renovation, smoking, and survey year were significant predictors of floor PbD [the proportion of variability in the dependent variable accounted for by the model (R2)=35%]. A similar set of predictors plus the presence of large areas of exterior deteriorated paint in pre-1950 homes and the presence of interior deteriorated paint explained 20% of the variability in sill PbD. A companion article [Dixon et al. Environ Health Perspect 117:468-474 (2009)] describes the relationship between children's blood lead and PbD.
Most houses with children have PbD levels that comply with federal standards but may put children at risk. Factors associated with PbD in our population-based models are primarily the same as factors identified in smaller at-risk cohorts. PbD on floors and windowsills should be kept as low as possible to protect children.
在美国,受铅污染的室内灰尘是儿童铅暴露的主要来源。1999年至2004年期间,国家健康与营养检查调查(NHANES)收集了12至60个月大儿童家庭的灰尘铅(PbD)负荷样本。
在本研究中,我们旨在将全国的PbD水平与现有的基于健康的标准进行比较,并确定与地板和窗台PbD相关的住房和人口统计学因素。
我们使用NHANES的PbD数据(来自地板的n = 2065,来自窗台的n = 1618)和协变量构建线性和逻辑回归模型。
人口加权的地板和窗台PbD几何平均值分别为0.5微克/平方英尺[几何标准误差(GSE)= 1.0]和7.6微克/平方英尺(GSE = 1.0)。只有0.16%的地板和4.0%的窗台的PbD达到或高于当前联邦标准,分别为40和250微克/平方英尺。收入、种族/族裔、地板表面/状况、窗台PbD、建造年份、近期翻新、吸烟和调查年份是地板PbD的重要预测因素[模型解释的因变量变异性比例(R2)= 35%]。一组类似的预测因素加上1950年前房屋大面积外部油漆老化以及内部油漆老化可解释窗台PbD变异性的20%。一篇配套文章[迪克森等人。《环境健康展望》117:468 - 474(2009)]描述了儿童血铅与PbD之间的关系。
大多数有孩子的房屋的PbD水平符合联邦标准,但仍可能使儿童面临风险。在我们基于人群的模型中,与PbD相关联的因素与在较小的高危队列中确定的因素基本相同。应尽可能降低地板和窗台上的PbD以保护儿童。