Harvard T.H. Chan School of Public Health, Boston, Massachusetts (Ms Cluett); Maine Medical Center for Outcomes Research and Evaluation, Maine Medical Center Research Institute, Portland, Maine (Dr Fleisch); Muskie School of Public Service, University of Southern Maine, Portland, Maine (Ms Decker); Maine Childhood Lead Poisoning Prevention Unit (Mr Frohmberg) and Maine Environmental and Occupational Health Program (Dr Smith), Maine Center for Disease Control, Augusta, Maine.
J Public Health Manag Pract. 2019 Jan/Feb;25 Suppl 1, Lead Poisoning Prevention:S76-S83. doi: 10.1097/PHH.0000000000000869.
There are limited data on the nature of environmental lead hazards identified during residential inspections for child blood lead levels (BLLs) of less than 10 μg/dL. We compare inspection findings for child BLLs of 5 to 9 μg/dL versus 10 μg/dL or more.
We reviewed inspection reports in Maine from September 2016 to March 2018. We used continuity-adjusted or Fisher's exact test for categorical variables and Wilcoxon rank-sum tests for continuous variables to compare differences in child, family, household, and lead hazard characteristics between BLL categories (5-9 μg/dL vs ≥10 μg/dL). We used Spearman correlation coefficients to assess relationships between home surface lead dust measurements and BLLs.
Of 351 residential inspections, 272 (77%) were for children with BLLs of 5 to 9 μg/dL. Children with BLLs of 5 to 9 μg/dL as compared with children with BLLs of 10 μg/dL or more were less likely to chew window sills and door frames (8% vs 21%; P = .01), but otherwise were similar with respect to other established risk factors for lead poisoning. Children with BLLs of 5 to 9 μg/dL tended to have fewer paint hazards inside their homes (64% vs 78%; P = .03), and they were more likely to have dust-only hazards (8% vs 3%) or no identified lead paint hazards (23% vs 15%), though these differences were not statistically significant. For children with BLLs of 5 to 9 μg/dL, BLL was weakly correlated with average window sill dust level (Spearman r = 0.16; P = .01) and average floor dust level (r = 0.13; P = .03), but these correlations were not observed for children with BLLs of 10 μg/dL and higher.
We have found that inspections of homes of children with BLLs of 5 to 9 μg/dL are nearly as likely to identify lead hazards that require abatement as inspections of homes of children with BLLs of 10 μg/dL.
在对儿童血铅水平(BLL)低于 10μg/dL 的住宅进行检查时,有关环境铅危害性质的资料有限。我们比较了 BLL 为 5 至 9μg/dL 与 10μg/dL 或更高水平的检查结果。
我们对 2016 年 9 月至 2018 年 3 月期间缅因州的检查报告进行了审查。我们使用连续校正或 Fisher 精确检验比较了 BLL 类别(5-9μg/dL 与≥10μg/dL)之间儿童、家庭、家庭和铅危害特征的差异。我们使用 Spearman 相关系数评估家庭表面铅尘测量值与 BLL 之间的关系。
在 351 次住宅检查中,有 272 次(77%)是针对 BLL 为 5 至 9μg/dL 的儿童进行的。与 BLL 为 10μg/dL 或更高的儿童相比,BLL 为 5 至 9μg/dL 的儿童更不可能啃咬窗台和门框(8%对 21%;P=0.01),但其他铅中毒的既定危险因素相似。BLL 为 5 至 9μg/dL 的儿童家中的油漆危害往往较少(64%对 78%;P=0.03),而且更有可能存在仅灰尘危害(8%对 3%)或未发现含铅油漆危害(23%对 15%),尽管这些差异无统计学意义。对于 BLL 为 5 至 9μg/dL 的儿童,BLL 与平均窗台灰尘水平(Spearman r=0.16;P=0.01)和平均地板灰尘水平(r=0.13;P=0.03)呈弱相关,但在 BLL 为 10μg/dL 及更高水平的儿童中未观察到这些相关性。
我们发现,对 BLL 为 5 至 9μg/dL 的儿童的家庭进行检查,几乎与对 BLL 为 10μg/dL 的儿童的家庭进行检查一样,都有可能发现需要进行整治的铅危害。