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RESEARCH AND PRACTICE |
Dennis Y. Kim, Gerald Curtis, and Sharunda Buchanan are with the Lead Poisoning Prevention Branch, Division of Environmental Hazards and Health Effects, National Center for Environmental Health, Centers for Disease Control and Prevention, Atlanta, Ga. Dennis Y. Kim is also with the Epidemic Intelligence Service, Division of Applied Public Health Training, Epidemiology Program Office, Centers for Disease Control and Prevention. Forrest Staley is with the Childhood Lead Poisoning Prevention Program, Jefferson County Department of Environmental Health, Louisville, Ky.
Correspondence: Requests for reprints should be sent to Dennis Y. Kim, MD, MPH, Lead Poisoning Prevention Branch, Division of Environmental Hazards and Health Effects, National Center for Environmental Health, Centers for Disease Control and Prevention, 1600 Clifton Rd, Mail Stop E-25, Atlanta, GA 30333 (e-mail: dmk4{at}cdc.gov).
| INTRODUCTION |
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| METHODS |
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Centrus Desktop software (Sagent Technology Inc, Mountain View, Calif) was used to geocode addresses. We used ArcView 3.2 software (Environmental Systems Research Institute, Redlands, Calif) to link geocoded addresses to the property valuation administrator's Real Estate Master File, a tax assessor database from the Louisville and Jefferson County Information Consortium that contains information on each house's year of construction, assessment value, and other historical data.
Housing built before 1900 was categorized as built in 1900. Housing coded as "pre-50" (before 1950) or "post-49" (1950 or later) was used only for analyses that stratified the houses as old or new rather than by decade. Houses worth less than $50 000 were considered lesser valued, and those worth $50 000 or more were higher valued. An elevated blood lead level was defined as 10 µg/dL or greater. We included children aged 12 to 71 months and used the first blood lead test. The relation among child blood lead levels, child age, housing value, and year of house construction was analyzed with SAS (SAS Institute Inc, Cary, NC).
| RESULTS |
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Children living in old houses had higher geometric mean blood lead levels than did children living in new houses (6.4 µg/dL vs 4.3 µg/dL, P < .001). More children living in old housing had elevated blood lead levels (4406; 28%), compared with those living in new housing (1794; 9%) (odds ratio [OR] = 3.79; 95% confidence interval [CI] = 3.56, 4.02; Figure 1
). From 1900 to 1980, the older the house, the higher the mean blood lead level of resident children and the greater the proportion of resident children with elevated blood lead levels (Table 1
).
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| DISCUSSION |
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Children living in lesser-valued houses were at greater risk of having elevated blood lead levels, suggesting that lesser-valued homes are more likely to have dilapidated paint. However, housing age does not indicate the condition of the paint or reflect recent remodeling that could increase a child's risk.5 Therefore, for a given house age, a lesservalued house is more likely to represent a lead exposure risk to children. Although low income is a known risk factor for elevated blood lead levels, housing value intuitively appears to be a better marker of risk.
Our study had several limitations, including missing information on children's race/ethnicity and the source of lead exposure. Older houses may not have been the source of exposure if they had received lead abatement treatment or were in good condition. Information on alternative sources of exposure, such as parental occupation, nontraditional medicines, and folk remedies, was not available. House values from the tax assessor data might be incorrect. Finally, because we grouped houses built before 1900 into 1 category, those houses might require further stratified analysis.
The Centers for Disease Control and Prevention recommend targeted screening based on housing age, especially for houses built before 1950 or before 1978 with recent renovation.6 Our results suggested that screening might be improved by considering the decade the house was built or the house's value. Geographic information systems technology can be used to link tax assessor information to better stratify children's risk and might be used further in strategic planning for lead screening, helping local programs identify high-risk areas to better target screening of children.
| Footnotes |
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Each author contributed to the planning of the study, the data acquisition and analysis, and the writing and editing of the paper.
Accepted for publication November 21, 2001.
| References |
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2. Pirkle JL, Kaufmann RB, Brody DJ, Hickman T, Gunter EW, Paschal DC. Exposure of the US population to lead, 19911994. Environ Health Perspect.1998;106:745750.[Medline]
3. Reissman DB, Staley F, Curtis GB, Kaufmann RB. Use of geographic information system technology to aid health department decision making about childhood lead poisoning prevention activities. Environ Health Perspect.2001;109:8994.[Medline]
4.
16 CFR part 1303 and
1500.17.
5. Centers for Disease Control and Prevention. Occupational and take-home lead poisoning associated with restoring chemically stripped furnitureCalifornia, 1998. MMWR Morb Mortal Wkly Rep.2001;50:246248.[Medline]
6. Centers for Disease Control and Prevention. Screening Young Children for Lead Poisoning: Guidance for State and Local Public Health Officials. Atlanta, Ga: Public Health Service; 1997.
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