Faculty Bibliography

OBJECTIVE--To test the hypothesis that a reduction of 1000 ppm or more of lead in soil accessible to children would result in a decrease of at least 0.14 mumol/L (3 micrograms/dL) in blood lead levels. SETTING--Urban neighborhoods with a high incidence of childhood lead poisoning and high soil lead levels. DESIGN--Randomized controlled trial of the effects of lead-contaminated soil abatement on blood lead levels of children followed up for approximately 1 year after the intervention. PATIENTS--A total of 152 children less than 4 years of age with venous blood lead levels of 0.34 to 1.16 mumol/L (7 to 24 micrograms/dL). Children were largely poor and had a mean age at baseline of 32 months, a mean blood lead level of 0.60 mumol/L (12.5 micrograms/dL), and a median surface soil lead level of 2075 ppm. INTERVENTIONS--Children were randomized to one of three groups: the study group, whose homes received soil and interior dust abatement and loose paint removal; comparison group A, whose homes received interior dust abatement and loose paint removal; and comparison group B, whose homes received only interior loose paint removal. MAIN OUTCOME MEASURES--Change in children's blood lead levels from preabatement levels to levels approximately 6 and 11 months after abatement. RESULTS--The mean decline in blood lead level between preabatement and 11 months after abatement was 0.12 mumol/L (2.44 micrograms/dL) in the study group (P = .001), 0.04 mumol/L (0.91 microgram/dL) in group A (P = .04), and 0.02 mumol/L (0.52 microgram/mL) in group B (P = .31). The mean blood lead level of the study group declined 0.07 mumol/L (1.53 micrograms/dL) more than that of group A (95% confidence interval [CI], -0.14 to -0.01 mumol/L [-2.87 to -0.19 micrograms/dL]) and 0.09 mumol/L (1.92 micrograms/dL) more than group B (95% CI, -0.16 to -0.03 mumol/L [-3.28 to -0.56 micrograms/dL]). When adjusted for preabatement lead level, the 11-month mean blood lead level was 0.06 mumol/L (1.28 micrograms/dL) lower in the study group as compared with group A (P = .02) and 0.07 mumol/L (1.49 micrograms/dL) lower than in group B (P = .01). The magnitude of the decline independently associated with soil abatement ranged from 0.04 to 0.08 mumol/L (0.8 to 1.6 micrograms/dL) when the impact of potential confounders, such as water, dust, and paint lead levels, children's mouthing behaviors, and other characteristics, was controlled for. CONCLUSIONS--These results demonstrate that lead-contaminated soil contributes to the lead burden of urban children and that abatement of lead-contaminated soil around homes results in a modest decline in blood lead levels. The magnitude of reduction in blood lead level observed, however, suggests that lead-contaminated soil abatement is not likely to be a useful clinical intervention for the majority of urban children in the United States with low-level lead exposure

OBJECTIVE--To examine changes in the prevalence and distribution of childhood asthma and its relationship with various measures of children's health and functioning between 1981 and 1988. It was hypothesized that there would be an increase in the prevalence of asthma, especially among black children, and that available measures would suggest a deterioration in the health and functioning of children with asthma over this period. DESIGN--Analyses of data from the Child Health Supplements to the National Health Interview Survey. SETTING AND SAMPLE--Nationally representative random sample of 15,224 children aged 0 to 17 years in 1981 and 17,110 in 1988. MAIN OUTCOME MEASURES--Changes in (1) the prevalence and distribution of asthma, and (2) among children with asthma, the percentage of children hospitalized, days spent in bed, school days lost in the year prior to survey, and parent ratings and reports of children's overall health status and behavior problems. RESULTS--The estimated prevalence of childhood asthma increased from 3.1% in 1981 to 4.3% in 1988 (P < .0001), with similar increases for children, adolescents, and both sexes. Increases occurred among white children (2.7% to 4.1%; P < .0001) but not black children (5.3% vs 5.1%; not significant). Among those with asthma in 1988 compared with 1981, there was better overall health status (11% vs 24% fair/poor; P < .0001) and fewer with 30 or more days spent in bed in the last year (3.9% vs 7.2%; P < .04). We also observed trends toward a lower rate of hospitalization in the last year (10% vs 14%; P = .07), fewer school days missed (2% vs 6% with > 30 days; P = .08), and a lower rate of extreme behavior problem scores (13% vs 18%; P = .09) in 1988 compared with 1981. Reductions were similar among both black and white children. CONCLUSIONS--These results indicate that the estimated prevalence of asthma among children in the United States increased by almost 40%, and that although the increase occurred exclusively among white children, the prevalence of asthma still remains higher in black children than in white children. There was no support for increasing asthma severity and functional impact among either black or white children with asthma in 1988 compared with 1981. These findings provide no evidence to support the beliefs that asthma prevalence is increasing largely among black children or that the severity of asthma among most children in the United States is increasing

Numerous health consequences of children's exposure to maternal smoking have been demonstrated, including increased rates of low birth weight, infant mortality, respiratory infections, asthma, and modest impairments of cognitive development. There is little evidence, however, linking maternal smoking and increased rates of children's behavior problems. Data from the population-based National Longitudinal Survey of Youth were used to investigate the possible association of maternal smoking and behavior problems among 2256 children aged 4 through 11 years. In multiple regression analyses the authors controlled for child's race, age, sex, birth weight, and chronic asthma; family structure, income, and divorce or separation in the prior 2 years; mother's education, intelligence, self-esteem, employment status, chronic disabling health conditions, and use of alcohol during pregnancy; and the quality of the home environment as assessed by the Home Observation for Measurement of the Environment-Short Form to investigate the relationship between maternal smoking and children's behavior problems. The measure of maternal smoking status reflected two levels of smoking intensity (less than a pack per day and a pack or more per day) for each of three different categories of children's exposure: prenatal only (mother smoked only during pregnancy), passive only (mother smoked only after pregnancy), and prenatal plus passive exposure (mother smoked both during and after pregnancy). Measures of children's behavior problems included the overall score on a 32-item parent-reported child Behavior Problem Index (PBI), scores on the BPI's subscales, and rates of extreme scores on the BPI.(ABSTRACT TRUNCATED AT 250 WORDS)