Michael Rabinowitz

Environmental correlates of infant blood lead levels in Boston.

From a blood lead survey of 11,837 births, 249 newborns were enrolled in a 2-year, longitudinal study. Their blood leads (PbB) were measured semiannually, and their homes were visited for repeated collections of dust, soil, indoor air, tap water, and paint. Recent refinishing activity and the sizes of nearby streets were recorded. Overall mean PbB was 7.2 micrograms/dl (SD = 5.3) at birth. PbB did not vary systematically with age. Each subjects average postnatal PbB correlated highly with the amount of lead in dust (r = 0.4, P less than 0.0001) and soil (r = 0.3, P less than 0.001), and with the lead in paint (r = 0.2, P less than 0.01). Dust, soil and air lead levels correlated with one another. Refinishing activity in the presence of lead paint was associated with elevations of PbB. Water lead, proximate traffic, weight of recovered dust, race, maternal age and education, and sex were not predictive of PbB. Multivariate models of PbB were constructed that become increasingly predictive with age (r2 = 20 to 37%). Indoor dust lead, lead in soil, refinishing activity, and season were the independent variables.

Lead in Milk and Infant Blood: A Dose-Response Model

As part of a longitudinal study of the sources and developmental effects of current urban lead exposure, lead was measured in tap water from the homes of 249 infants, in 100 breast milk samples, and in 73 samples of the infant formula used by non-nursing mothers. Also, the blood lead levels of the infants who received these fluids were determined at birth and at 6 months of age. Among the infants who were breast fed, the lead content of their milks correlated very well with their 6-month blood lead levels (r = .42, P = .0003). The mean lead content of infant formulas and breast milk were not significantly different, nor was the blood lead of children fed one or the other. Lead levels in maternal milk correlated poorly with umbilical cord blood lead (r = .18, P = .10). Tap water and infant blood lead levels correlated minimally (r = .11, P = .10). Since milk represents much of the diet of young infants and because breast milk lead levels are stable, it is possible to relate blood lead and daily dosage in this population.

Relationships between serial blood lead levels and exfoliated tooth dentin lead levels: Models of tooth lead kinetics

SummaryBecause bones and permanent teeth accumulate lead, exfoliated deciduous teeth have been utilized as retrospective markers of cumulative exposure in epidemiological surveys. In this paper we describe four models of lead uptake by the coronal dentin of shed primary teeth, each with different assumptions and ramifications. Each model is characterized by different relationships between blood lead at several ages and tooth lead. Values observed in our cohort of normal Boston children are most compatible with models positing the largest lead contribution coming at older ages (i.e., closer to age at exfoliation). Characteristics of models incompatible with our data include (1) lead deposition only during initial calcification and (2) no loss or resorption of lead.

Stable Isotopes of Lead for Source Identification

Lead is unique among all the metals in having variations among mining districts in the relative abundances of its stable (non-radioactive) isotopes. Since first described in 1927, many applications have been reported, mostly for geological uses. More recently archeological, environmental, bio-kinetic and public health uses have been found. The abundances of the four stable isotopes are usually determined with specialized mass spectrometry using rapid mass scanning cycles or multiple collectors. The relative abundances are commonly expressed as 206/204, 206/207, and 206/208 atomic ratios. Precision of 0.5% for 206/204 and even better (0.03%) for the other pairs are obtainable. The three ratios co-vary strongly and depend on when the ore was formed. This provides a tracer for following a particular batch of lead, since the ratio can only change when the lead is mixed with a different lead. A major limitation of this method is that it is useful only to those problems where the potential sources are isotopically distinct and few in number. The covariance of the ratios usually allows for only two sources to be considered. Potential sources can often be ruled out.

Delayed appearance of tracer lead in facial hair.

Three adult men were fed 204 Pb - a rare, stable isotope of lead - daily for about 100 days. Simultaneous blood and facial hair measurements of this tracer and of total lead concentrations were made by mass spectrometric isotope dilution analysis. Although the blood showed an immediate response to the intake of the tracer, the facial hair showed a more gradual response and a delay of approximately 35 days. Since the pattern of appearance of lead in hair does not appear to represent a simple time delay of blood lead concentration, the existence of a physiological pool of lead fed by the blood and giving rise to the content in hair is suggested. Hair lead values should, therefore, be interpreted as the integral of the blood lead values over the mean life of this intermediate pool - about 100 days.

Lead in umbilical blood, indoor air, tap water, and gasoline in Boston.

A strong statistical correlation was found among the monthly averages of lead concentrations in umbilical cord blood (about 500 births/month), indoor air (12 sites/month), and gasoline lead sales between March, 1980 and April, 1981 in Boston. Tap water lead (24/month) variations did not correlate with blood lead in this population.

Relating tooth and blood lead levels in children

Lead concentrations in shed teeth have found increasing utility in research studies of lead exposure and child development. Teeth are useful because they record lead levels and are easily collected. However, in considering internal doses of lead, most of what has been learned about human lead toxicity and kinetics has been expressed in terms of blood lead concentrations. For example, a computerized literature search found {open_quotes}blood lead{close_quotes} as a key word in 1,035 articles cited between January and October 1994. Only 9 articles were found for {open_quotes}tooth lead{close_quotes}. Because of the advantages of using teeth to assess lead exposure, the relation between teeth and blood lead levels deserves more attention. 14 refs., 1 fig., 1 tab.

Lead and childhood propensity to infectious and allergic disorders: Is there an association

Lead appears to impair both antibody and cellular responses of laboratory animals to a variety of bacteria. These immunosuppressive effects of lead appear at levels below those associated with overt toxicity, and might, therefore, be present among urban children exposed to subtoxic amounts of lead. To examine the role of lead exposure on rates of infectious and allergic diseases in children, the authors compared the prevalence of these illnesses in children classified by the lead level in the umbilical cord blood, and in the dentine of their deciduous teeth. Information about illness was obtained from a mailed questionnaire completed by parents.

Dentin as a possible bio-epidemiological measure of exposure to mercury

The subtle human health effects from prolonged exposure to small amounts of mercury vapor are unknown. It has been difficult to study possible effects of low-dose exposure for lack of a good measure of long-term exposure. Current methods which use blood, urine, hair, and nails reliably measure only recent exposures. Long-term exposure to lead has been measured using levels found in human dentin. The purpose of this study was to determine whether mercury also accumulates in dentin. In this study, dentin from 16 human teeth, all without dental amalgam restorations, was analyzed by thermal neutron activation analysis. The teeth were selected from people with and without dental mercury amalgam restorations elsewhere in their dentitions. Mercury was found in amounts up to 5.9 ppm. While the highest mercury level was from a sample from someone who had dental amalgam restorations elsewhere in their dentition, the second highest was from someone who had no amalgam restorations. Also, a sample which was not used for any statistical comparisons but which was analyzed because the tooth contained an amalgam restoration had one of the lowest levels of mercury. These results, while inconclusive due to a small sample size, suggest that inorganic mercury vapor is a relatively small contributor to the overall body burden of mercury.

Children's classroom behavior and lead in Taiwan

Lead has long been recognized to cause adverse effects on children. A recent compilation of studies on the correlation of child intelligence and low-level lead exposure has demonstrated a robust dose-response relationship. Teeth have frequently been used as a retrospective marker of lead exposure. The pediatric neurotoxicity of lead is not limited to intelligence, but also effects other behaviors which are apparent to classroom teachers. The present study provided an opportunity to evaluate a range of relatively lower lead exposures, including those near smelters as well as those living in more typical urban and rural conditions. This may reveal help identify the lowestor no-effect levels.