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Childhood Lead Toxicity Morri Markowitz, MD
Learning Objectives After completing this module, faculty will be able to teach students and residents to develop a basic understanding of:
General Principles of Lead Toxicity Case Study Every pediatric provider should be able to recognize the clinical signs of lead poisoning. The following vignette is an example of how such a case might present in your practice. A 2-year-old female came into the emergency room with a three-week history of intermittent abdominal pain, loss of appetite, vomiting, constipation, and increasing apathy. One week prior she had been seen in her pediatrician's office with the same complaints. An evaluation found that the child resided in an old house with peeling paint. The pediatrician had reassured the mother that the child was probably suffering from intestinal flu, but did obtain a blood sample that was sent to a commercial lab for analysis. There were no focal or abnormal findings on physical examination in the ER, with the exception of a pulse of 140 and a lethargic but awake child who would not cooperate with the examiner. Within a few minutes of evaluation, the child developed major motor seizures and suffered a cardiopulmonary arrest. She was intubated and successfully resuscitated. At that point the ER physician called the lab and determined that a lead level had been ordered by the pediatrician the week before. The sample had been processed on the day the pediatrician ordered it; results indicated a lead level >200 mcg/dL. Neither the child's pediatrician nor the laboratory had followed through on the results of the ordered test. Chelation and supportive therapy were begun. Characteristics of Lead Lead (Pb) has an atomic number of 82, an average atomic weight of 207, and a melting point of 327ƒ C. At room temperature, it is a white soft metal. Lead can be found in oxidation states 0, +2 and +4, but it is the +2 form that is of biological concern. Although organic lead compounds (tetraethyl lead) have been used as gasoline additives, inorganic lead compounds are the species of current concern. Sources and Uses of Lead Lead in paint is the most common source of environmental exposure. Because lead makes paint more durable, the metal was, for many decades, routinely used as an additive. Although its detrimental health effects were recognized early in the twentieth century, it was not until 1976 that use of lead in paint was legally limited to formulations intended for marine use or for areas prone to excessive weathering, such as bridges. However, leaded paint from the old formulation remains in an estimated 25-40 million U.S. homes. In addition to its restricted paint uses, lead is currently used in vehicular batteries, cable sheathing, chemicals, and many construction materials. The permissible amount of lead in gasoline produced for use in the United States was reduced by 90% a decade ago, to 0.1 mcg/L. Meanwhile, leaded gasoline continues to be used in much of the developing world. Lead has also been found to be a component of several cosmetics and folk remedies in use in Latin America, the Mideast, and Asia. Travelers from these areas may bring these sources with them when they visit or immigrate to the United States. Routes of Delivery The gastrointestinal tract serves as the primary route of entry into the body. Lead fumes may be inhaled, resulting in the absorption of very small particles through the lung. Hand-to-mouth behavior can result in ingestion of lead-containing dust or paint chips. Children may also drink contaminated water or swallow phlegm contaminated with inhaled lead. Organic lead can be absorbed transcutaneously but inorganic lead, the type found in paint, is poorly absorbed through the skin. Susceptibility The occurance of lead poisoning depends on the developmental stage, behavior, nutritional status, and metabolism of an exposed individual. The exercise on the following page reviews some of the different factors affecting a child's susceptibility.
Effects of Lead on the Body Biochemical Lead exerts its effects through several biochemical mechanisms. The diversity of these mechanisms is such that virtually all cells are affected by this metal.
The relationship between lead and enzymes of the heme pathway, which is found in all cells, has been well studied. At least three of the seven enzymes in this pathway are poisoned by lead, resulting in diminished production of heme and in the buildup of substrate. Because these substrates may be toxic when present in excessive amounts, the detrimental effects of lead may be multiplied by the presence of abnormally high levels of normal biochemical constituents of the cell. Increased erythrocyte levels of the heme precursor protoporphyrin (EP) are used as a marker of lead toxicity; EP levels greater than 35 mcg/dL are associated with lead levels greater than 25-50 mcg/dL. There is, however, a delay of several weeks between the beginning of lead exposure and its accumulation in the body and consequent rise in EP levels. Another heme pathway enzyme affected by lead is ALA dehydratase. ALA dehydratase activity and susceptibility to inhibition by lead varies between individuals and is transmitted as an autosomal genetic trait. Blood lead concentrations as low as 15 mcg/dL inhibit this enzyme in susceptible children. Of interest is the observation that reduction of blood lead levels by treatment is associated with an immediate reversal of this toxic effect. Thus, ALA-dehydratase activity can be used longitudinally as a marker of the success of treatment. Subclinical Epidemiological studies conducted in the U.S. population have shown subclinical effects in both height and hearing in children with blood lead levels in the range of 0-40 mcg/dL. As blood lead increases by 10 mcg/dL, children are, on average, about 1 cm shorter than the genetic potential would otherwise predict. It should be emphasized that this is a subclinical finding; the effect is not large enough to bring the average child to the endocrinologist for evaluation of short stature. Similarly, hearing at all frequencies decreases as blood lead levels increase. Again, this is a subclinical finding. Typically there is no complaint of deafness from the parents of a mild/moderately lead-poisoned child. Rather, parents describe a child who won't listen. Perhaps the most critical subclinical effects of lead poisoning are observed in the cognition and behavior of children. The effect on cognition is most pronounced when exposures occur in utero or in the first years of life.
In addition, the blood lead level at approximately two years of age has been shown to correlate with future results on cognitive testing performed 2-8 years later. The magnitude of the relationship has varied between studies but averages about 0.5 (i.e., for every 1 mcg/dL increase in the blood lead level at age 2 years, the cognitive test score is reduced by 0.5 units). The lag between time of elevation in blood lead levels and time of adverse impact on cognitive test results is noteworthy. In longitudinal studies, blood lead levels measured at the time of cognitive testing (ages 2, 5, 7, or 10 years) did not correlate with results of intelligence tests, such as the Bayley or McCarthy Scales of Children's Abilities.
Clinical Symptoms and signs related to specific organ systems - particularly the gastrointestinal tract and central nervous system - are found in children with elevated blood lead levels. The clinical symptoms of lead poisoning, however, are found in less than 1% of all children with blood lead levels of 10 mcg/dL or higher, and generally become apparent only late in the progression of the disorder.
Diagnosis A three-pronged approach is needed to diagnose clinical symptoms of lead poisoning:
Screening The current gold standard for determining whether lead absorption has occurred is a measurement of the blood lead level. Blood lead has been chosen because, as the body's highway for the distribution of this metal, it reflects the confluence of absorption, entry to and from soft and hard tissue stores, and renal filtration. Of the methods currently available for detecting lead absorption, it is also the easiest to perform. A blood lead level >10 mcg/dL is considered elevated (CDC, 1991). Until 1997, the CDC recommended universal screening of all preschool children using this method. Subsequently, given the fall in prevalence of lead poisoning, the CDC revised its guidelines. Blood lead screening is now based on local risk assessment of exposure to lead. It is up to state and local health departments to determine the level of risk and to issue policy guidelines for providers. In the absence of formal local guidance, "universal screening should be carried out" (CDC,1997). This means that all children should be screened by blood lead measurement at 12 and 24 months of age, and at 36-72 months of age if not previously screened. Where local risk has been defined and found to be low, targeted screening may suffice. Minimum Personal Risk Questionnaires (see table below from CDC, 1997) may be used as a first-pass screening method, followed by blood lead testing if the answers indicate high risk. Overall, the sensitivity of questionnaires designed to identify lead-poisoned children is about 60-70%. Sensitivity can be improved when local conditions are considered and locally appropriate questions are added.
Minimum Personal Risk Questionnaire
Alternatively, selection for blood lead testing may be based on residence in a geographic area known to have large amounts of lead or on membership in a high-risk group, such as indigent children. Follow-Up If initial blood testing finds the child's blood lead level to be >10 mcg/dL, then careful follow-up is mandatory. The following table, derived from the 1997 CDC statement "Screening Young Children for Lead Poisoning" summarizes the timing of follow-up to the screening test.
If the diagnostic screening test confirms an elevated blood lead level, then the following is recommended:
Other methods of assessment The blood concentration of a metal is not fully predictive of the amount of the metal in a critical organ such as the brain, and symptoms for a given blood lead level may vary greatly among individuals. Other methods are available to assess the presence of lead in the body. Measuring lead in urine:
This drug-induced urinary lead excretion has been correlated with bone lead content as well as blood lead levels; the higher the blood or bone lead, the more likely a large lead diuresis will be induced by the drug. It may therefore reflect body stores of lead as well as a fraction of that lead which is mobile, i.e., not bound in the deep crystalline compartment of bone, and hence, potentially more likely to produce toxic effects. Use of CaNa2 EDTA as a diagnostic agent has been formalized in the Lead Mobilization Test (LMT). The test consists of the administration of a standard dose of CaNa2 EDTA (e.g. 500 mg/m 2 once, given IM or IV; if IM it is first mixed 1:1 by volume with 1% procaine), followed by a timed (6-8 hour) urine collection for Pb content determination. If the response to the drug is a large Pb excretion, then a full course of chelation is immediately begun. It is likely that children selected for chelation on the basis of this test will excrete considerably more lead during the course of treatment then they would have excreted spontaneously, that their blood lead levels will decline, and that enzyme function will improve in the short-term. It has not, however, been determined whether chelating children on the basis of a positive LMT alters the long-term course of their disease. Although performed successfully at some clinical centers, the LMT is not currently recommended by the American Academy of Pediatrics as part of the evaluation process of lead-poisoned children. Measuring lead in bone:
The photons emitted from the bone are counted and a quantitative estimate of the bone lead content is thus obtained. Unfortunately, few such instruments are available nationally and their use is generally restricted to clinical research. Treatment There are four components to the treatment of lead poisoning: environmental control, behavior modification, nutrition counseling, and chelation therapy. Environmental control The most important action is to eliminate the source of lead exposure, thereby inhibiting further poisoning. Since leaded paint is the most common source of environmental exposure, the child should not be allowed access to areas with flaking, lead-based paint until these surfaces are repaired and the lead-containing paint removed. Abatement procedures should be carefully performed; otherwise, leaded dust can be disseminated throughout the home and local neighborhood, increasing the health risk to occupants. Once removal of the lead-containing paint is complete, ongoing clean-up with a lead-binding detergent and a high efficiency particle air (HEPA) vacuum is essential. Behavior modification Since lead must find some way of entry into the body in order to cause health problems, behavioral modification directed toward both parent and child may be helpful. The parent should be instructed to clean dust and loose paint from surfaces before and after abatement procedures, as described in the preceding section. The parent should also closely observe the child in order to inhibit the hand-to-mouth activity that accounts for most ingestion of lead. Washing the child's hands before eating will also help to remove surface lead before it can be ingested. Nutrition counseling Nutrition influences the amount of lead absorbed by the intestine as well as the effects of this metal on the body. A diet deficient in calcium and iron may enhance lead absorption, retention, and toxicity. Therefore, the clinician should determine the child's daily intake of these elements and correct deficiencies either by dietary modification or with mineral supplements. It has been suggested that other dietary components, such as fat intake, may affect lead absorption, but little data exists to support these contentions. Chelation therapy Chelation therapy is the use of drugs to bind lead and enhance its excretion. The CDC currently advises chelation for children with blood lead levels of 45 mcg/dL or greater. Four drugs are now available for chelation. Two of these can be given orally: succimer (DMSA, Chemet) and penicillamine (PCA, Cuprimine). Of these oral agents, only succimer is FDA-approved for the treatment of lead-poisoned children with levels >45 mcg/dL. The other two drugs must be administered parenterally: calcium disodium edetate (CaNa2EDTA), given IV or IM; and BAL (Dimercaprol), given IM. Each of these medicines has its own toxicity profile, but serious adverse effects are rare and generally reversible. Side effects, such as rashes and blood dyscrasias, are of greatest concern with penicillamine use, but generally they can generally be minimized when the drug is administered by a knowledgeable practitioner. The long-term efficacy of chelation therapy for any group of asymptomatic lead-poisoned children has yet to be fully evaluated. However, the well-defined subclinical and biochemical toxicity induced by lead in children with elevated blood levels <45 mcg/dL, and the metal's potential for causing permanent cognitive deficits, have prompted some experts to chelate moderately lead-poisoned children (blood lead 20-45 mcg/dL). This response is determined either on the basis of blood lead levels alone, or in conjunction with the results of other diagnostic tests, such as the Lead Mobilization Test (LMT). Children who undergo the LMT and have a large lead excretion are treated immediately with a full course of chelation, as indicated earlier. Blood lead levels fall rapidly but temporarily with chelation therapy. Most children exhibit a rebound in their blood lead levels within days to weeks of completion of treatment. Levels eventually stabilize somewhere between the pretreatment peak and immediate post-treatment trough. Without chelation treatment, but with cessation of ingestion, blood lead levels will also eventually fall as a function of aging in most children. Presumably, this fall in blood lead levels reflects a declining lead content in critical organs, and reduced toxicity. Active treatment (with or without chelation) over three to six months is associated with a fall in blood and bone lead measures and an improvement in cognitive scores and behavior (Ruff, 1993). Learning Methods This material is best suited for lecture format with interactive questions. It may be used for Grand Rounds presentations. Evaluation Methods Increased awareness of the potential sources of lead poisoning should be reflected in the medical records. Chart reviews may determine whether parents and children have been asked age-appropriate questions on possible exposures to lead, and whether blood lead screening has been performed. Bibliography Agency for Toxic Substances and Disease Registry. U.S. Department of Health and Human Services. The Nature and Extent of Lead Poisoning in Children in the United States: A Report to Congress. Atlanta, GA: ATSDR (1988). Bellinger D, Leviton A, Waternaux C, Needleman H, Rabinowitz M. Longitudinal analysis of prenatal and postnatal lead exposure and early cognitive development. N Engl J Med 316:1037-1043 (1987). Centers for Disease Control and Prevention: Preventing Lead Poisoning in Young Children: A Statement by the Centers for Disease Control. Atlanta, GA: CDC (1991). Centers for Disease Control and Prevention: Screening Young Children for Lead Poisoning: Guidance for State and Local Public Health Officials. Atlanta, GA: CDC (1997). Centers for Disease Control and Prevention. Update: blood lead levels - United States, 1991-1994. MMWR 46:141 -145 (1997). Needleman HL, Gatsonis CA. Low-level lead exposure and the IQ of children. JAMA 263:673-678 (1990). Needleman HL, Riess JA, Tobin MJ, Biesecker GE, Greenhouse JB. Bone lead levels and delinquent behavior. JAMA 275: 363-369 (1996). Pirkle JL, Brody DJ, Gunter EW, Kramer RA, Paschal DC, Flegal KM, Matte TD. The decline in blood lead levels in the United States: the National Health and Nutrition Examination Surveys (NHANES). JAMA 272(4):284-291 (1994). Ruff HA, Bijur PE, Markowitz ME, Ma Y, Rosen JF: Declining blood lead levels and cognitive changes in moderately lead-poisoned children. JAMA 269:1641-1646 (1993). |
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