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Childhood lead poisoning: Clinical manifestations and diagnosis

Childhood lead poisoning: Clinical manifestations and diagnosis
Literature review current through: Jan 2024.
This topic last updated: Aug 19, 2022.

INTRODUCTION — The clinical manifestations and diagnosis of lead toxicity will be reviewed here.

Prevention and treatment of lead poisoning are discussed separately. (See "Childhood lead poisoning: Exposure and prevention" and "Childhood lead poisoning: Management".)

EPIDEMIOLOGY — Lead (Pb), a stable metallic element with an atomic number of 82 and atomic weight of 207, was first smelted around 4000 BC as a byproduct of silver processing [1]. The consequences of lead toxicity have been recognized for millennia [2]. Despite this knowledge, lead was included as an ingredient of gasoline in the 1920s and continued to be used in paint in some developed countries until the 1970s [3,4]. In many low-income countries, lead in gasoline and industrialized uses of lead (eg, smelters, mines, or refineries) remain major sources of exposure [1]. About 50 percent of the worldwide burden of lead poisoning occurs in Southeast Asia [5]. In 2021, UNICEF estimated that one in three children, globally, had blood lead levels (BLLs) >5 mcg/dL (0.24 micromol/L) [1,6].

Risk factors, sources, and prevention of childhood lead poisoning include:

Risk factors – Children younger than six years of age (and particularly those younger than 36 months) are more susceptible to the toxic effects of lead than are adults because they have an incomplete blood-brain barrier that permits the entry of lead into the developing nervous system, and because they have a greater prevalence of iron deficiency, which can result from and cause lead poisoning through increased absorption of lead from the gastrointestinal tract [7-9]. In addition, they are at greater risk of exposure to lead dust because of crawling, higher respiratory rates, and hand-to-mouth behavior.

The prevalence of elevated BLLs is highest among urban children who live in deteriorating housing that was built before the 1970s, and children exposed to lead as a result of industrialized use (eg, aerosolized lead from smelters or refineries or lead in water near mining operations) [1,10,11]. Lead poisoning is more common among urban than rural children, low-income than middle-income children, and children who live in older housing [11-16]. While the prevalence of elevated BLLs has decreased over time, disparities in the geometric mean of BLLs continue when assessing for ethnicity and income level. In the United States, Black children continue to have a statistically higher BLL compared with other populations. In addition, the prevalence of lead poisoning is increased among refugee children who have arrived recently in the United States, and among children entering foster care [17,18].

Sources – Children typically are exposed to environmental lead through ingestion or inhalation. Common sources include chips of paint or lead dust from lead-painted surfaces; food or beverages purchased, stored, or served in lead-soldered cans or lead-glazed pottery; water from lead-soldered plumbing; automobile emissions; and lead-using industry (table 1). Although the United States phased out lead-soldered food cans during the 1980s, imported canned goods may still contain lead [10]. Less common sources of lead exposure include herbal and folk medications, imported crayons and other toys, mini blinds, cosmetics, jewelry, and imported cookware [10,16,19]. Parental take-home exposures may also result in elevated BLLs in children [20]. Adolescents may have an increased risk due to hobbies and occupational exposures in firing ranges and lead dust that accumulates in these facilities [21]. (See "Childhood lead poisoning: Exposure and prevention".)

Prevention – Removal of the common sources of lead exposure has resulted in declining BLLs in children. As an example, in the United States, as lead was removed from gasoline and paint, the average BLL in children decreased from 16 mcg/dL (0.77 micromol/L) to less than 3 mcg/dL (0.14 micromol/L) in 1991 [12,22]. This trend in declining BLL in United States children less than five years of age has continued with the estimated geometric mean of 0.67 mcg/dL [23,24] in 2018 [25]. Residual lead from these and other products remains in the environment because elemental lead cannot be degraded. In many resource-limited parts of the world, lead continues to be used in gasoline, pigment (eg, in paint, cosmetics, and crayons), pottery glaze, solder, cooking vessels, jewelry, toys, and even medications [5]. These products occasionally are imported into the United States and are potential sources of lead exposure. Although the incidence and severity of lead poisoning in the United States are decreasing, an estimated 450,000 children in the United States were above the reference value of 3.5 mcg/dL (0.14 micromol/L) in 2021 [26]. (See "Childhood lead poisoning: Exposure and prevention", section on 'Prevention'.)

TOXICOLOGY — The key aspects determining toxicity are based upon blood lead levels (BLLs), the disposition of lead once it enters the body (toxicokinetics), and molecular toxicology as follows:

Toxic level – The American Academy of Pediatrics and the Centers for Disease Control and Prevention (CDC) state that no safe or "nontoxic" BLL exists. In the United States, a reference level corresponding to the 97.5th percentile of BLLs in children in the United States (3.5 mcg/dL [0.14 micromol/L] as of 2021) has been adopted [26]. The reference level should not be mistaken for an "action" level as this terminology has changed based on the science that has shown lead to be more toxic than previously thought. Between 1970 and 2012, the toxic level or "action" level was gradually decreased from 60 mcg/dL (2.9 micromol/L) to 10 mcg/dL (0.48 micromol/L). In 2012, the CDC, recognizing that no safe blood level existed, established a reference level at the 97.5th percentile of BLLs in children in the United States (3.5 mcg/dL [0.14 micromol/L] as of 2021) (table 2). The decrease in 1991 was prompted by evidence of cognitive and behavioral effects of low-level lead toxicity [27,28]. Changes in the definition of the toxic level have been accompanied by changes in policies for screening, treatment, and prevention [29]. (See "Screening tests in children and adolescents", section on 'Lead poisoning' and "Childhood lead poisoning: Management".)

Toxicokinetics – Inorganic lead is not metabolized but is directly absorbed, distributed, and excreted. The absorption of lead depends upon the route of exposure and the age and nutritional status of the exposed individual [10]. Inhaled lead may either be cleared by cilia, resulting in ingestion, or retained by the lung (30 to 50 percent) for rapid and complete absorption [30]. Children absorb a greater proportion of lead from the gastrointestinal tract than do adults (up to 70 versus 20 percent) [31,32]. Fasting, iron deficiency, and calcium deficiency also may increase the gastrointestinal absorption of lead [10,33,34].

Lead that is absorbed from the gastrointestinal or respiratory tracts is distributed by a three-compartment model to the blood, soft tissues, and bone (trabecular and cortical). The half-life of lead varies depending upon the body compartment and the age of the child [10,30,35-38].

On average, the half-life in each compartment is:

Blood – 28 to 36 days

Soft tissue – 40 days

Mineralizing tissues – Greater than 25 years

Lead that is not retained in the tissues is excreted by the kidneys or through biliary clearance into the gastrointestinal tract. Children younger than two years of age retain approximately one-half of absorbed lead, whereas adults ultimately retain only 1 percent [10]. More than 70 percent of the total body burden of lead in children is contained in the mineralized tissues [10,39]. Thus, the BLL is not a good reflection of the total body lead burden. In general, the concentration of lead in other organs is comparable to that found in blood. Approximately 99 percent of the lead in blood is bound to red blood cells. The remaining 1 percent (ie, plasma lead) serves as an intermediate in transporting lead from the erythrocytes to other body compartments.

The lead in mineralizing tissues accumulates in two subcompartments: a labile compartment that readily exchanges lead with the blood, and an inert pool [38]. The inert pool of lead can be mobilized during periods of physiologic stress (eg, pregnancy, lactation, fractures, chronic disease) and represents an endogenous source of lead that can maintain an elevated BLL long after the exogenous exposure source has been removed [10]. Because the body accumulates lead over a lifetime and releases it slowly, lead toxicity may occur without a major acute exposure.

Molecular toxicology – Lead is a potent toxic substance with no apparent threshold [40]. Lead interferes with the interactions of divalent cations and sulfhydryl groups. It has widespread physiologic effects because most biochemical reactions are regulated by these agents [41,42]. In vitro, many of the reactions in which lead serves as a competitive inhibitor are reversible. However, in vivo, downstream events lead to cell death and irreversible damage at the cellular level, particularly in the central nervous system [43-45].

Lead can disrupt signal transduction cascades by activating protein kinase C, competing with magnesium and inhibiting cyclic nucleotide hydrolysis by phosphodiesterases, or inhibiting function at the N-methyl-D-aspartate-type glutamate receptor [46-49]. Lead also can uncouple mitochondrial oxidative phosphorylation in the central nervous system [45,50].

Magnetic resonance spectroscopy (MRS) in individuals with elevated BLLs demonstrates reduction in the N-acetylaspartate/creatine and phosphocreatine ratios in the frontal gray matter, suggesting that lead poisoning affects metabolism in the brain [51,52].

Lead competes with calcium for entry into synaptosomes [53] and interacts with numerous receptor-activated and voltage-gated cation channels [54,55]. In addition, lead increases the infidelity of DNA and RNA polymerase, leading to somatic and germline mutations [56,57]. Lead-exposed rodents have an increased incidence of cancer [58-63]. However, this association has not been found in humans [64-66].

Hematologic complications of lead toxicity result from the ability of lead to directly inhibit delta-aminolevulinic acid dehydratase (ALAD), enzymes necessary for heme biosynthesis, and ferrochelatase, a mitochondrial sulfhydryl enzyme causing increased urinary delta-aminolevulinic acid (ALA), urinary coproporphyrin, and erythrocyte zinc protoporphyrin [67-70]. The enzymatic blocks responsible are partial. While anemia may not be seen until blood lead concentrations are markedly elevated, the effect on hemoglobin synthesis occurs at lower levels [10]:

ALA dehydratase is inhibited at very low BLLs with no threshold yet apparent.

Elevation of erythrocyte protoporphyrin occurs at levels of 30 mcg/dL (1.48 micromol/L).

Reduced hemoglobin synthesis is found in children at levels of 40 (1.93 micromol/L) and in adults at levels of 50 mcg/dL (2.41 micromol/L), respectively.

The basophilic stippling of red cells is due to the presence of aggregated ribosomes, which may also include mitochondrial fragments. Conditions, such as lead poisoning, can result in altered ribosomes to have a higher propensity to aggregate. With staining, this appears as increased basophilic granulation (picture 1) [71].

CLINICAL MANIFESTATIONS — Lead affects at least three major organ systems (see 'Toxicology' above):

Central and peripheral nervous systems

Heme biosynthetic pathway

Renal system with injury to the renal and cardiovascular systems closely related

In the child, the most serious symptoms are found in the central nervous system with subtle effects (eg, decreased intelligence quotient [IQ] and cognitive effects) occurring at lower levels and severe effects (eg, seizures, encephalopathy) occurring at higher levels. The majority of children with elevated blood lead concentrations will be asymptomatic from overt clinical manifestations of lead poisoning. Symptoms will vary depending upon the acuity of the lead exposure and the age of the exposed individual (table 3) [10].

The clinical manifestations of lead poisoning in adults are discussed separately. (See "Lead exposure, toxicity, and poisoning in adults", section on 'Clinical manifestations'.)

Neurologic — Neurologic effects of lead poisoning in children include:

Neurobehavioral deficits – Detectable blood lead levels (BLLs) are associated with neurocognitive deficits, and a lower limit for these effects has not been established in population studies. While blood lead tests may result below 5 mcg/dL (0.24 micromol/L), there is no safe lead level, and none should be considered "normal." Low-level lead poisoning may lead to permanent central nervous system injury in young children [72]. Population-based studies consistently have shown that BLLs greater than 10 mcg/dL (0.48 micromol/L) affect the cognitive and behavioral development of children [27,28,73-81]. However, neurocognitive effects also have been demonstrated at even lower BLLs, and no threshold is known to exist [82-86]. Data suggests environmental lead exposure in children at blood lead concentrations <7.5 mcg/dL (0.36 micromol/L) is associated with cognitive deficits. Furthermore, studies suggest that a permanent pattern of cognitive dysfunction may result from lead poisoning in the first several years of life [87], and in-utero lead exposure may adversely affect infant neurodevelopment (measured at 24 months) independent of postnatal BLL [88,89].

The neurobehavioral effects of lead poisoning appear to persist, at least in part, into adolescence and adulthood, despite a decline in BLL [28,75,90-96]. As an example, in a longitudinal cohort study of over 1000 patients, lead exposure, based upon BLL at eleven years of age (mean BLL 11 mcg/dL [0.53 micromol/L]), was associated in a dose-dependent fashion with lower IQ and lower socioeconomic status at age 38 years despite adjustment for maternal IQ, child IQ, and childhood socioeconomic status [97,98]. These studies are contradicted, however, by others that state the magnitude of these effects are small and cannot be interpreted at the individual child [95,99,100]. Although studies cannot predict performance in an individual child with elevated BLL [101], it is clear that primary prevention of lead exposures can prevent the adverse neurotoxic effects of lead.

However, evidence also identifies other important variables besides elevated BLLs when assessing intelligence that may better explain the decline of intellectual abilities, such as parental and social environments [95,100].

Acute encephalopathy – Acute encephalopathy occurs at BLLs greater than 100 to 150 mcg/dL (4.8 to 7.2 micromol/L) and is indicated by persistent vomiting, altered or fluctuating state of consciousness, ataxia, seizures, or coma. Cerebral edema is a variable finding, more often present in younger than older children. Children with lead encephalopathy may develop inappropriate antidiuretic hormone secretion [102], partial heart block [103], and marked decrease in renal function. (See 'Renal' below.)

Hearing loss – The hearing loss occurs primarily in the higher frequencies and may contribute to learning and behavior problems [10,104]. (See "Hearing loss in children: Screening and evaluation".)

Peripheral neuropathy – Peripheral neuropathy, rare in children with isolated lead poisoning, is more common in children with concomitant sickle cell anemia [105-108]. Decreased nerve conduction velocity occurs at BLLs as low as 20 mcg/dL (1 micromol/L) [109,110].

Renal — In the child, lead appears to have an effect on renal function even at levels below 10 mcg/dL (0.48 micromol/L). This is especially true if the lead exposure occurs over a sustained period of time. Subtle abnormalities in renal tubular function, associated with aminoaciduria, glycosuria, and increased excretion of low-molecular weight proteins can occur [111]. Lead nephropathy, which is characterized histologically by chronic interstitial nephritis, is a potential complication of prolonged high-level lead exposure. In addition, current levels of lead exposure have the potential for lead-related nephrotoxicity, primarily in adults with diabetes, hypertension, or underlying chronic kidney disease. These issues, including the long-term renal outcomes of childhood lead poisoning, are discussed in detail separately. (See "Lead nephropathy and lead-related nephrotoxicity".)

Gastrointestinal — Lead colic, which includes sporadic vomiting, intermittent abdominal pain, and constipation, may occur [105].

Endocrine — BLLs and vitamin D levels are inversely related as lead interferes in the formation of active vitamin D, which has an important role in its influence on calcium metabolism. Calcium is under tight homeostatic control in all cells [10,112]. Vitamin D metabolism is decreased at BLLs of 30 mcg/dL (1.45 micromol/L) [112]. The effects of lead toxicity on cell growth and maturation and tooth and bone development probably are mediated through the effects on vitamin D [10]. Likewise, because of the similar biochemical nature between lead and calcium, increased absorption of lead can occur, especially in children who have decreased calcium intake.

Hematologic — Lead poisoning in children rarely results in anemia [10]. The two major mechanisms are decreased hemoglobin synthesis and hemolysis. Decreased hemoglobin synthesis has been well documented at BLLs of 40 mcg/dL (1.9 micromol/L) [113] and is caused by the interference of lead with several enzymatic steps in the heme pathway. With prolonged exposure to high levels of lead, red blood cell survival is diminished. Acute, high-level lead poisoning (BLL >70 mcg/dL [3.4 micromol/L]) has been associated with hemolytic anemia [10]. Increased erythrocyte destruction is more marked in adults than in children. Increased red cell fragility and decreased osmotic resistance may be observed. The degree of hemolysis is insufficient to produce jaundice. (See 'Toxicology' above and "Approach to the child with anemia".)

Anemia in children with lead poisoning may in fact be caused by iron deficiency because lead poisoning and iron deficiency have similar risk factors [114,115]. Anemia secondary to lead toxicity usually is mild, hemolytic, and normocytic. In contrast, anemia secondary to iron deficiency is hypochromic, microcytic, and reticulocytopenic [116,117]. (See "Iron deficiency in infants and children <12 years: Screening, prevention, clinical manifestations, and diagnosis".)

DIAGNOSIS — Lead poisoning is diagnosed by an elevated venous blood lead level (BLL). Specific interventions for lead poisoning start at BLLs ≥3.5 mcg/dL (0.14 micromol/L), the current reference level as designated by the Centers for Disease Control and Prevention (CDC). (See 'Lead levels' below.)

Specific treatment of childhood lead poisoning depends upon the degree of the blood lead elevation, the presence of symptoms, and local resources available for lead abatement. (See "Childhood lead poisoning: Management".)

Asymptomatic patients — The diagnosis of lead toxicity usually is made through a lead screening program because most children with lead toxicity do not have overt clinical symptoms although neurobehavioral abnormalities may be present. (See "Screening tests in children and adolescents", section on 'Lead poisoning'.)

Symptomatic patients — The symptoms of lead toxicity by level of exposure are shown in the table (table 3). They include cognitive impairment, language delay, and behavior problems at low concentrations and progress to vomiting, colicky abdominal pain, fatigue, renal insufficiency, and encephalopathy at higher concentrations. Lead poisoning should be included in the differential diagnosis for children with any of these complaints or conditions [118].

Encephalopathy — When a patient presents with an acute onset of persistent vomiting, alteration of mental status, and/or seizures consistent with lead encephalopathy and a BLL cannot be obtained emergently, one or more of the following clinical findings constitute strong supportive evidence for a diagnosis of lead poisoning and permit emergency initiation of chelation therapy pending confirmation by blood lead testing [119,120]:

Age one to five years

Prodrome of gastrointestinal symptoms with progression from lethargy to encephalopathy

History of pica, prior increased lead levels, or other history of lead exposure

Strongly positive qualitative urine coproporphyrin

Elevated erythrocyte protoporphyrin

Basophilic stippling of peripheral red blood cells or erythroblasts in the bone marrow (picture 1)

Hypophosphatemia

Glycosuria

Lead flecks on abdominal radiograph (image 1)

Lead lines on long-bone radiographs (image 2)

Children with lead encephalopathy almost always have elevated blood erythrocyte protoporphyrin (EP) or zinc protoporphyrin (ZPP) concentrations (>35 mcg/dL) [121]. Both are precursors of heme and become elevated as lead inhibits heme synthesis [122]. Thus, elevated EP or ZPP concentrations can be used as a rapid confirmatory test in most hospitals. However, it should be noted that elevated ZPP is usually not seen until the BLL is above 30 mcg/dL and may not be elevated in acute exposures given the delay from lead's effect on heme synthesis. (See 'Erythrocyte protoporphyrin' below.)

Emergency treatment should begin if encephalopathy secondary to severe lead toxicity is suspected. A BLL should be obtained to confirm the diagnosis, but treatment should not be delayed while awaiting the result. (See "Childhood lead poisoning: Management", section on 'Symptomatic lead poisoning'.)

EVALUATION

History — A careful history should be obtained from the families of all children suspected of toxic lead exposure (table 4). The history should include:

Onset and severity of symptoms of toxicity (table 3)

Nutritional history with particular attention to intake of iron and calcium

History of pica

Family history of lead poisoning

Foreign birthplace and recent foreign residence with attention to refugee status [123-126]

Assessment of potential sources of lead exposure: work history of the parents/primary caregivers and other significant caregivers, hobbies, age of the home and history of home renovations, source of water supply, location and condition of play areas, use of imported or glazed ceramics, imported jewelry and cosmetics, and proximity to industrial facilities or hazardous waste sites (table 1)

Physical examination — There are few specific findings on physical examination that can help identify the presence of lead poisoning:

Delayed language development and neurobehavioral dysfunction are important features and should raise concern for lead poisoning when present.

Lethargy is particularly concerning because it indicates encephalopathy.

Lead lines, at the junction of the teeth and gums, are rarely seen. If present, they usually indicate severe and prolonged lead exposure (picture 2) [10].

Laboratory evaluation

Lead levels — The laboratory evaluation of the child with lead poisoning should include a repeat venous blood lead level (BLL) to confirm the diagnosis. BLLs should also be obtained in the patient's siblings, housemates, and/or playmates. Parents/primary caregivers may also require testing, especially if the child is an infant who is not crawling or is breastfeeding. All family members should be tested if the source is not found to be from peeling paint chips or soil because household items (eg, cosmetics, jewelry, pottery, or spices) are shared by everyone in the home. Confirmatory samples should be obtained through venous sampling and processed in lead-free collection tubes. The phlebotomy site should be carefully cleaned with an alcohol wipe to remove any lead from the skin surface.

Capillary blood sampling is simpler than venous blood sampling for lead screening and is a valid collection method if it is performed properly [127]. However, capillary samples are subject to contamination with exogenous lead and can yield false-positive results. Common causes of falsely elevated BLLs from capillary lead sampling include [128]:

Inadequate use of gloves by phlebotomists

Use of alcohol wipes contaminated with lead-based ink

Inadequate cleansing of the child's finger

Failure to wipe off the first drop of blood

The limit of detection of point-of-care tests are such that lead levels below 5 mcg/dL (0.24 micromol/L) may not be accurate [129]. Despite the reference level set by the Centers for Disease Control and Prevention (CDC; 3.5 mcg/dL [0.14 micromol/L]), the response to an elevated BLL should remain the same and is dependent on the resources available to local and state health departments. Despite potential inaccuracy, point-of-care tests are still our preferred method of lead screening because their use is associated with much higher screening rates [130].

All patients who have elevated BLLs on capillary samples must have confirmatory venous blood testing. However, an elevated capillary blood lead result may indicate lead in the environment and proceeding with anticipatory guidance for reducing lead risk is appropriate pending confirmation.

Federal regulations in the United States permit laboratories that perform BLL testing to operate with an allowable error of ±4 mcg/dL (0.19 micromol/L) or 10 percent, whichever is greater [131,132]. As an example, a laboratory that meets proficiency standards may report an actual BLL of 8 mcg/dL (0.38 micromol/L) as any value ranging from 4 to 12 mcg/dL (0.19 to 0.58 micromol/L).

Bone and dentine lead levels, measured by K x-ray fluorescence spectroscopy or atomic absorption spectroscopy, respectively, are better indicators of the child's total lead burden than BLLs [38,73,90]. However, these tests are not routinely available and are not recommended by the CDC [133]. BLLs remain the gold standard for the diagnosis of lead poisoning in children. (See 'Diagnosis' above.)

Erythrocyte protoporphyrin — Erythrocyte protoporphyrin (EP), typically assayed as zinc protoporphyrin (ZPP), is elevated (greater than 35 mcg/dL) in iron deficiency, lead poisoning, many erythrocyte disorders, and porphyria. Thus, it is not diagnostic for lead poisoning. EP levels usually are not elevated until lead levels are greater than 30 mcg/dL (1.45 micromol/L) [10,134,135]. Thus, EP is not a good screening test for mild lead toxicity and is not recommended for screening for pediatric lead poisoning.

  • EP can be helpful to diagnose moderate to severe lead poisoning and determine the acuity of the exposure as follows:

An EP ≥250 mcg/dL (4.44 micromol/L) in a patient with findings suggestive of lead encephalopathy supports the initiation of emergency chelation in situations where the results of a venous BLL are not rapidly available [136-138]. (See "Childhood lead poisoning: Management", section on 'Symptomatic lead poisoning'.)

EP can also help identify the acuity of lead exposure when measured along with a venous BLL. If the BLL is markedly elevated but the EP is normal, then lead exposure is acute [139]. However, if both the BLL and EP are elevated, then the exposure is likely chronic [140]. Thus an EP is suggested for all children with a BLL that warrants chelation (>45 mcg/dL [2.17 micromol/L]) (table 5). However, if the results of EP testing are not rapidly available, chelation should proceed based upon the BLL.

The pattern of decline in EP in lead poisoned patients who have received chelation provides information regarding the level of body burden of lead. However, there is a delay in the decrease in EP after chelation due to delayed recovery of the heme synthesis pathway when it has been inhibited by elevated lead levels.

Additional tests — In patients with elevated BLLs, screening for iron deficiency anemia should also occur (eg, complete blood count, ferritin, and C-reactive protein) [133]. (See "Iron deficiency in infants and children <12 years: Screening, prevention, clinical manifestations, and diagnosis", section on 'Laboratory screening'.)

Additional tests are necessary for children who require chelation therapy (see "Childhood lead poisoning: Management", section on 'Initial evaluation' and "Childhood lead poisoning: Management", section on 'Pharmacologic agents for chelation'):

Serum electrolytes

Blood urea nitrogen and creatinine

Serum calcium and magnesium

Alanine and aspartate aminotransferases

Urinalysis

In addition, screening for glucose-6-phosphate dehydrogenase (G6PD) deficiency should be performed in patients who will be treated with dimercaprol or succimer and who have risk factors or findings consistent with the disease. (See "Childhood lead poisoning: Management" and "Diagnosis and management of glucose-6-phosphate dehydrogenase (G6PD) deficiency".)

Diagnostic imaging — A plain abdominal radiograph should be obtained in symptomatic children or those with a history of pica or acute ingestion of lead-containing objects (eg, fishing weights) to identify leaded objects (eg, lead toys, leaded paint chip, or lead flecks in the stool).

Radio-opaque lead flecks in the intestinal tract suggesting recent ingestion are found inconsistently (image 1). However, their presence may have implications for treatment at the time of diagnosis [119]. (See "Childhood lead poisoning: Management".)

The CDC does not recommend obtaining long-bone radiographs in the evaluation of children with lead exposure [133]. Lead lines at the end of growing long bones (image 2) are found only in children with BLLs greater than 45 mcg/dL (2.2 micromol/L). Thus, long-bone radiographs are not useful as part of the diagnostic evaluation of children with lower BLLs and are not used as a diagnostic tool, routinely, in children with lead levels greater than 45 mcg/dL.

Computed tomography of the head should be obtained in children with signs of lead encephalopathy to assess for findings of increased intracranial pressure.

Magnetic resonance imaging in adults with chronic elevated BLLs has shown decreased myelination and white matter loss [141].

MANAGEMENT — The management of childhood lead poisoning is discussed separately. (See "Childhood lead poisoning: Management".)

ADDITIONAL RESOURCES

Lead poisoning management resources — To identify a physician and other clinicians with expertise in managing childhood lead poisoning, contact the regional health department, regional poison control center, or, in the United States, a Pediatric Environmental Health Specialty Unit.

In the United States, additional sources for information for the general public and professionals include the Centers for Disease Control and Prevention (CDC; 1-800-CDC-INFO [800-232-4636]), Pediatric Environmental Health Specialty Units, and the National Lead Information Center (1-800-424-LEAD [5323]).

Regional poison control centers — Regional poison control centers in the United States are available at all times for consultation on patients with known or suspected poisoning, and who may be critically ill, require admission, or have clinical pictures that are unclear (1-800-222-1222). In addition, some hospitals have medical toxicologists available for bedside consultation. Whenever available, these are invaluable resources to help in the diagnosis and management of ingestions or overdoses. Contact information for poison centers around the world is provided separately. (See "Society guideline links: Regional poison control centers".)

Society guideline links — Links to society and government-sponsored guidelines from selected countries and regions around the world are provided separately. (See "Society guideline links: Lead and other heavy metal poisoning".)

SUMMARY AND RECOMMENDATIONS

Clinical manifestations – In children, the most serious symptoms of lead poisoning affect the central nervous system with subtle effects (eg, decreased intelligence quotient [IQ] and cognitive effects) occurring at lower levels and severe effects (eg, seizures, encephalopathy) occurring at higher levels. The majority of children with elevated blood lead concentrations will be asymptomatic from overt clinical manifestations of lead poisoning. If present, symptoms will vary depending upon the acuity of the lead exposure and the age of the exposed individual (table 3). (See 'Clinical manifestations' above.)

Diagnosis – The diagnosis and evaluation of lead poisoning depends upon whether or not symptoms of lead poisoning are present:

Symptomatic patients – Lead poisoning can cause diverse and nonspecific symptoms such as vomiting, cognitive impairment, language delay, hearing loss, and behavior problems at low concentrations and colicky abdominal pain, anemia, intellectual disability, seizures, renal insufficiency, and encephalopathy at higher concentrations (table 3). Lead poisoning should be included in the differential diagnosis for children with any of these complaints or conditions. (See 'Symptomatic patients' above.)

Symptomatic lead intoxication is a medical emergency warranting an emergency repeat venous blood lead level (BLL) for confirmation, emergency evaluation, hospitalization, and chelation. The laboratory evaluation for these patients is described separately. (See "Childhood lead poisoning: Management", section on 'Initial evaluation'.)

When a patient presents with an acute onset of persistent vomiting, alteration of mental status, and/or seizures consistent with lead encephalopathy and a stat BLL is not available, one or more of the following clinical findings constitutes strong supportive evidence for a diagnosis of lead poisoning and permits emergency initiation of chelation therapy pending confirmation by blood lead testing (see 'Encephalopathy' above and "Childhood lead poisoning: Management", section on 'Symptomatic lead poisoning'):

-Age one to five years

-Prodrome of gastrointestinal symptoms with progression from lethargy to encephalopathy

-History of pica, prior increased lead levels, or other history of lead exposure

-Strongly positive qualitative urine coproporphyrin

-Elevated erythrocyte or zinc protoporphyrin

-Basophilic stippling of peripheral red blood cells or erythroblasts in the bone marrow (picture 1)

-Hypophosphatemia

-Glycosuria

-Lead flecks on abdominal radiograph (image 1)

-Lead lines on long-bone radiographs (image 2)

Asymptomatic patients – The diagnosis of lead poisoning in asymptomatic patients usually is made through measurement of an elevated BLL during routine blood lead screening. False-positive elevation caused by contamination of the fingertip can occur if capillary samples are obtained. (See 'Asymptomatic patients' above.)

All patients who have elevated BLLs on capillary samples must have confirmatory venous blood testing that are collected in lead-free tubes. Management decisions should only be based upon venous blood lead results (table 6). (See 'Lead levels' above and "Childhood lead poisoning: Management".)

The limit of detection of point-of-care tests are such that lead levels below 5 mcg/dL (0.24 micromol/L) may not be accurate. Despite the reference level set by the Centers for Disease Control and Prevention (CDC; 3.5 mcg/dL [0.14 micromol/L]), the response to an elevated BLL should remain the same and is dependent on the resources available to local and state health departments.

Evaluation of asymptomatic patients – In asymptomatic patients with elevated BLLs, additional evaluation includes (see 'Evaluation' above):

Careful history (table 4) and physical examination to assess for subtle signs of lead poisoning. (See 'History' above and 'Physical examination' above.)

Screening for iron deficiency anemia (eg, complete blood count, ferritin, and C-reactive protein). (See 'Additional tests' above and "Iron deficiency in infants and children <12 years: Screening, prevention, clinical manifestations, and diagnosis", section on 'Laboratory screening'.)

Additional studies for asymptomatic children who require chelation therapy (see 'Additional tests' above and "Childhood lead poisoning: Management"):

-Serum electrolytes

-Blood urea nitrogen and creatinine

-Serum calcium and magnesium

-Alanine and aspartate aminotransferases

-Urinalysis

-Screening for glucose-5-phosphate dehydrogenase (G6PD) deficiency in patients who will be treated with dimercaprol or succimer and who have risk factors or findings consistent with the disease (see "Childhood lead poisoning: Management", section on 'Pharmacologic agents for chelation')

A plain abdominal radiograph should be obtained in asymptomatic children with a history of pica or acute ingestion of lead-containing objects (eg, curtain or fishing weights). (See 'Diagnostic imaging' above.)

ACKNOWLEDGMENT

The editorial staff at UpToDate acknowledge both Richard L Hurwitz, MD and Dean A Lee, MD, PhD, who contributed to earlier versions of this topic review.

The UpToDate editorial staff acknowledges extensive contributions of Donald H Mahoney, Jr, MD to earlier versions of this topic review.

  1. Childhood lead poisoning working group. Childhood Lead Poisoning, World Health Organization, Geneva, Switzerland, 2010. http://apps.who.int/iris/bitstream/10665/136571/1/9789241500333_eng.pdf?ua=1&ua=1 (Accessed on April 29, 2020).
  2. Nriagu JO. Saturnine gout among Roman aristocrats. Did lead poisoning contribute to the fall of the Empire? N Engl J Med 1983; 308:660.
  3. Needleman HL. The removal of lead from gasoline: historical and personal reflections. Environ Res 2000; 84:20.
  4. Hernberg S. Lead poisoning in a historical perspective. Am J Ind Med 2000; 38:244.
  5. Lead poisoning and health. Fact sheet No 379. World Health Organization, August 2015. http://www.who.int/mediacentre/factsheets/fs379/en/ (Accessed on April 29, 2020).
  6. Rees N, Fuller R. The Toxic Truth: Children’s Exposure to Lead Pollution Undermines a Generation of Future Potential. 2020. The-Toxic-Truth-Childrens-Exposure-To-Lead-Pollution-UNICEF-Pure-Earth-2020.pdf (pureearth.org) http://www.pureearth.org/wp-content/uploads/2021/04/The-Toxic-Truth-Childrens-Exposure-To-Lead-Pollution-UNICEF-Pure-Earth-2020.pdf (Accessed on July 28, 2022).
  7. Wright RO, Tsaih SW, Schwartz J, et al. Association between iron deficiency and blood lead level in a longitudinal analysis of children followed in an urban primary care clinic. J Pediatr 2003; 142:9.
  8. Kwong WT, Friello P, Semba RD. Interactions between iron deficiency and lead poisoning: epidemiology and pathogenesis. Sci Total Environ 2004; 330:21.
  9. Kim Y, Park S. Iron deficiency increases blood concentrations of neurotoxic metals in children. Korean J Pediatr 2014; 57:345.
  10. Agency for Toxic Substances and Disease Registry. Case Studies in Environmental Medicine (CSEM): Lead Toxicity Cover Page. https://www.atsdr.cdc.gov/csem/csem.asp?csem=34&po=0 (Accessed on April 29, 2020).
  11. Raymond J, Wheeler W, Brown MJ, Centers for Disease Control and Prevention (CDC). Lead screening and prevalence of blood lead levels in children aged 1-2 years--Child Blood Lead Surveillance System, United States, 2002-2010 and National Health and Nutrition Examination Survey, United States, 1999-2010. MMWR Suppl 2014; 63:36.
  12. Centers for Disease Control and Prevention (CDC). Blood lead levels--United States, 1999-2002. MMWR Morb Mortal Wkly Rep 2005; 54:513.
  13. Melman ST, Nimeh JW, Anbar RD. Prevalence of elevated blood lead levels in an inner-city pediatric clinic population. Environ Health Perspect 1998; 106:655.
  14. Centers for Disease Control and Prevention (CDC). Blood lead levels in young children--United States and selected states, 1996-1999. MMWR Morb Mortal Wkly Rep 2000; 49:1133.
  15. Centers for Disease Control and Prevention (CDC). Update: blood lead levels--United States, 1991-1994. MMWR Morb Mortal Wkly Rep 1997; 46:141.
  16. Keller B, Faciano A, Tsega A, Ehrlich J. Epidemiologic Characteristics of Children with Blood Lead Levels ≥45 μg/dL. J Pediatr 2017; 180:229.
  17. Geltman PL, Brown MJ, Cochran J. Lead poisoning among refugee children resettled in Massachusetts, 1995 to 1999. Pediatrics 2001; 108:158.
  18. Chung EK, Webb D, Clampet-Lundquist S, Campbell C. A comparison of elevated blood lead levels among children living in foster care, their siblings, and the general population. Pediatrics 2001; 107:E81.
  19. Centers for Disease Control and Prevention (CDC). Infant lead poisoning associated with use of tiro, an eye cosmetic from Nigeria--Boston, Massachusetts, 2011. MMWR Morb Mortal Wkly Rep 2012; 61:574.
  20. Newman N, Jones C, Page E, et al. Investigation of Childhood Lead Poisoning from Parental Take-Home Exposure from an Electronic Scrap Recycling Facility — Ohio, 2012. MMWR Morb Mortal Wkly Rep 2015; 64:743.
  21. Centers for Disease Control and Prevention (CDC). Lead exposure from indoor firing ranges among students on shooting teams--Alaska, 2002-2004. MMWR Morb Mortal Wkly Rep 2005; 54:577.
  22. Annest JL. Trends in the blood lead levels of the US population. In: Lead Versus Health, Rutter M, Jones RR (Eds), John Wiley and Sons, New York 1983. p.33.
  23. Ruckart PZ, Jones RL, Courtney JG, et al. Update of the Blood Lead Reference Value - United States, 2021. MMWR Morb Mortal Wkly Rep 2021; 70:1509.
  24. Centers for Disease Control and Prevention. National Report on Human Exposure to Environmental Chemicals cgroup2_LBXBPB_2011-p.pdf (cdc.gov) https://www.cdc.gov/exposurereport/report/pdf/cgroup2_LBXBPB_2011-p.pdf (Accessed on July 28, 2022).
  25. Centers for Disease Control and Prevention (CDC). Blood lead levels in children aged 1-5 years - United States, 1999-2010. MMWR Morb Mortal Wkly Rep 2013; 62:245.
  26. Centers for Disease Control and Prevention. Blood lead reference value. https://www.cdc.gov/nceh/lead/data/blood-lead-reference-value.htm (Accessed on November 04, 2021).
  27. Bellinger D, Sloman J, Leviton A, et al. Low-level lead exposure and children's cognitive function in the preschool years. Pediatrics 1991; 87:219.
  28. Needleman HL, Schell A, Bellinger D, et al. The long-term effects of exposure to low doses of lead in childhood. An 11-year follow-up report. N Engl J Med 1990; 322:83.
  29. Centers for Disease Control and Prevention. Preventing lead poisoning in young children: a statement by the Centers for Disease Control, 1991.
  30. National Research Council. Measuring lead exposure in infants, children and other sensitive populations. 1993. National Academies Press.
  31. Alexander FW, Clayton BE, Delves HT. Mineral and trace-metal balances in children receiving normal and synthetic diets. Q J Med 1974; 43:89.
  32. Ziegler EE, Edwards BB, Jensen RL, et al. Absorption and retention of lead by infants. Pediatr Res 1978; 12:29.
  33. James HM, Hilburn ME, Blair JA. Effects of meals and meal times on uptake of lead from the gastrointestinal tract in humans. Hum Toxicol 1985; 4:401.
  34. Mahaffey KR. Environmental lead toxicity: nutrition as a component of intervention. Environ Health Perspect 1990; 89:75.
  35. Griffin TB, Coulston F, Wills H, Russell JC. Biologic effects of airborne particulate lead on continuously exposed rats and rhesus monkeys. Environ Qual Saf Suppl 1975; 2:202.
  36. Rabinowitz MB, Wetherill GW, Kopple JD. Kinetic analysis of lead metabolism in healthy humans. J Clin Invest 1976; 58:260.
  37. Griffin TB, Coulston F, Wills H, Russell JC. Clinical studies on men continuously exposed to airborne particulate lead. Environ Qual Saf Suppl 1975; 2:221.
  38. Hu H, Rabinowitz M, Smith D. Bone lead as a biological marker in epidemiologic studies of chronic toxicity: conceptual paradigms. Environ Health Perspect 1998; 106:1.
  39. Barry PS. A comparison of concentrations of lead in human tissues. Br J Ind Med 1975; 32:119.
  40. Lidsky TI, Schneider JS. Lead neurotoxicity in children: basic mechanisms and clinical correlates. Brain 2003; 126:5.
  41. Al-Modhefer AJ, Bradbury MW, Simons TJ. Observations on the chemical nature of lead in human blood serum. Clin Sci (Lond) 1991; 81:823.
  42. Johnson FM. The genetic effects of environmental lead. Mutat Res 1998; 410:123.
  43. Fox DA, Campbell ML, Blocker YS. Functional alterations and apoptotic cell death in the retina following developmental or adult lead exposure. Neurotoxicology 1997; 18:645.
  44. Fox DA, He L, Poblenz AT, et al. Lead-induced alterations in retinal cGMP phosphodiesterase trigger calcium overload, mitochondrial dysfunction and rod photoreceptor apoptosis. Toxicol Lett 1998; 102-103:359.
  45. He L, Poblenz AT, Medrano CJ, Fox DA. Lead and calcium produce rod photoreceptor cell apoptosis by opening the mitochondrial permeability transition pore. J Biol Chem 2000; 275:12175.
  46. Markovac J, Goldstein GW. Picomolar concentrations of lead stimulate brain protein kinase C. Nature 1988; 334:71.
  47. Johnston MV, Goldstein GW. Selective vulnerability of the developing brain to lead. Curr Opin Neurol 1998; 11:689.
  48. Srivastava D, Hurwitz RL, Fox DA. Lead- and calcium-mediated inhibition of bovine rod cGMP phosphodiesterase: interactions with magnesium. Toxicol Appl Pharmacol 1995; 134:43.
  49. Srivastava D, Fox DA, Hurwitz RL. Effects of magnesium on cyclic GMP hydrolysis by the bovine retinal rod cyclic GMP phosphodiesterase. Biochem J 1995; 308 ( Pt 2):653.
  50. Holtzman D, Hsu JS. Early effects of inorganic lead on immature rat brain mitochondrial respiration. Pediatr Res 1976; 10:70.
  51. Trope I, Lopez-Villegas D, Cecil KM, Lenkinski RE. Exposure to lead appears to selectively alter metabolism of cortical gray matter. Pediatrics 2001; 107:1437.
  52. Trope I, Lopez-Villegas D, Lenkinski RE. Magnetic resonance imaging and spectroscopy of regional brain structure in a 10-year-old boy with elevated blood lead levels. Pediatrics 1998; 101:E7.
  53. Cooper GP, Suszkiw JB, Manalis RS. Heavy metals: effects on synaptic transmission. Neurotoxicology 1984; 5:247.
  54. Zwart R, van Kleef RG, Van Hooft JA, et al. Cellular aspects of persistent neurotoxicants: effects of Pb2+ on neuronal nicotinic acetylcholine receptors. Neurotoxicology 1997; 18:709.
  55. Oortgiesen M, Leinders T, van Kleef RG, Vijverberg HP. Differential neurotoxicological effects of lead on voltage-dependent and receptor-operated ion channels. Neurotoxicology 1993; 14:87.
  56. Sirover MA, Loeb LA. Infidelity of DNA synthesis in vitro: screening for potential metal mutagens or carcinogens. Science 1976; 194:1434.
  57. Hoffman DJ, Niyogi SK. Metal mutagens and carcinogens affect RNA synthesis rates in a distinct manner. Science 1977; 198:513.
  58. Kobayashi N, Okamoto T. Effects of lead oxide on the induction of lung tumors in Syrian hamsters. J Natl Cancer Inst 1974; 52:1605.
  59. Kasprzak KS, Hoover KL, Poirier LA. Effects of dietary calcium acetate on lead subacetate carcinogenicity in kidneys of male Sprague-Dawley rats. Carcinogenesis 1985; 6:279.
  60. Buzard GS, Kasprzak KS. Possible roles of nitric oxide and redox cell signaling in metal-induced toxicity and carcinogenesis: a review. J Environ Pathol Toxicol Oncol 2000; 19:179.
  61. Koller LD, Kerkvliet NI, Exon JH. Neoplasia induced in male rats fed lead acetate, ethyl urea, and sodium nitrite. Toxicol Pathol 1985; 13:50.
  62. ZOLLINGER HU. [Renal adenoma and carcinoma produced by lead poisoning in rats, and relations to corresponding neoplastic formations in man]. Virchows Arch Pathol Anat Physiol Klin Med 1953; 323:694.
  63. Van Esch GJ, Kroes R. The induction of renal tumours by feeding basic lead acetate to mice and hamsters. Br J Cancer 1969; 23:765.
  64. DINGWALL-FORDYCE I, LANE RE. A FOLLOW-UP STUDY OF LEAD WORKERS. Br J Ind Med 1963; 20:313.
  65. Moore MR, Meredith PA. The carcinogenicity of lead. Arch Toxicol 1979; 42:87.
  66. Nelson DJ, Kiremidjian-Schumacher L, Stotzky G. Effects of cadmium, lead, and zinc on macrophage-mediated cytotoxicity toward tumor cells. Environ Res 1982; 28:154.
  67. Johnson DR, Foulkes EC, Hammond PB. The renal handling of delta-aminolevulinic acid in normal and lead-poisoning rabbits. Toxicol Appl Pharmacol 1976; 38:101.
  68. Hammond PB. Exposure of humans to lead. Annu Rev Pharmacol Toxicol 1977; 17:197.
  69. Campbell BC, Brodie MJ, Thompson GG, et al. Alterations in the activity of enzymes of haem biosynthesis in lead poisoning and acute hepatic prophyria. Clin Sci Mol Med 1977; 53:335.
  70. Astrin KH, Bishop DF, Wetmur JG, et al. delta-Aminolevulinic acid dehydratase isozymes and lead toxicity. Ann N Y Acad Sci 1987; 514:23.
  71. Rees DC, Duley JA, Marinaki AM. Pyrimidine 5' nucleotidase deficiency. Br J Haematol 2003; 120:375.
  72. Weitzman ML, Matte T., Homa D, et al. A Review of Evidence of Adverse Health Effects Associated with Blood Lead Levels <10 µg/dL in Children. Reported by Work Group of the Advisory Committee on Childhood Lead Poisoning Prevention to Centers for Disease Control and Prevention, in Preventing Lead Poisoning in Young Children, A statement by the Centers for Disease Control and Prevention, Atlanta, GA August 2005. http://www.cdc.gov/nceh/lead/ACCLPP/meetingMinutes/lessThan10MtgMAR04.pdf (Accessed on April 29, 2020).
  73. Needleman HL, Riess JA, Tobin MJ, et al. Bone lead levels and delinquent behavior. JAMA 1996; 275:363.
  74. Mendelsohn AL, Dreyer BP, Fierman AH, et al. Low-level lead exposure and behavior in early childhood. Pediatrics 1998; 101:E10.
  75. Dietrich KN, Krafft KM, Bornschein RL, et al. Low-level fetal lead exposure effect on neurobehavioral development in early infancy. Pediatrics 1987; 80:721.
  76. Dietrich KN, Berger OG, Succop PA, et al. The developmental consequences of low to moderate prenatal and postnatal lead exposure: intellectual attainment in the Cincinnati Lead Study Cohort following school entry. Neurotoxicol Teratol 1993; 15:37.
  77. Baghurst PA, McMichael AJ, Wigg NR, et al. Environmental exposure to lead and children's intelligence at the age of seven years. The Port Pirie Cohort Study. N Engl J Med 1992; 327:1279.
  78. Mendelsohn AL, Dreyer BP, Fierman AH, et al. Low-level lead exposure and cognitive development in early childhood. J Dev Behav Pediatr 1999; 20:425.
  79. Pocock SJ, Smith M, Baghurst P. Environmental lead and children's intelligence: a systematic review of the epidemiological evidence. BMJ 1994; 309:1189.
  80. Chen A, Cai B, Dietrich KN, et al. Lead exposure, IQ, and behavior in urban 5- to 7-year-olds: does lead affect behavior only by lowering IQ? Pediatrics 2007; 119:e650.
  81. Liu J, Liu X, Wang W, et al. Blood lead concentrations and children's behavioral and emotional problems: a cohort study. JAMA Pediatr 2014; 168:737.
  82. Lanphear BP, Dietrich K, Auinger P, Cox C. Cognitive deficits associated with blood lead concentrations <10 microg/dL in US children and adolescents. Public Health Rep 2000; 115:521.
  83. Canfield RL, Henderson CR Jr, Cory-Slechta DA, et al. Intellectual impairment in children with blood lead concentrations below 10 microg per deciliter. N Engl J Med 2003; 348:1517.
  84. Lanphear BP, Hornung R, Khoury J, et al. Low-level environmental lead exposure and children's intellectual function: an international pooled analysis. Environ Health Perspect 2005; 113:894.
  85. Téllez-Rojo MM, Bellinger DC, Arroyo-Quiroz C, et al. Longitudinal associations between blood lead concentrations lower than 10 microg/dL and neurobehavioral development in environmentally exposed children in Mexico City. Pediatrics 2006; 118:e323.
  86. Ji Y, Hong X, Wang G, et al. A Prospective Birth Cohort Study on Early Childhood Lead Levels and Attention Deficit Hyperactivity Disorder: New Insight on Sex Differences. J Pediatr 2018; 199:124.
  87. White RF, Diamond R, Proctor S, et al. Residual cognitive deficits 50 years after lead poisoning during childhood. Br J Ind Med 1993; 50:613.
  88. Gomaa A, Hu H, Bellinger D, et al. Maternal bone lead as an independent risk factor for fetal neurotoxicity: a prospective study. Pediatrics 2002; 110:110.
  89. CDC response to Advisory Committee on Childhood Lead Poisoning Prevention Recommendations in "Low Level Lead Exposure Harms Children: A Renewed Call of Primary Prevention" http://www.cdc.gov/nceh/lead/ACCLPP/activities.htm (Accessed on April 29, 2020).
  90. Fergusson DM, Horwood LJ, Lynskey MT. Early dentine lead levels and educational outcomes at 18 years. J Child Psychol Psychiatry 1997; 38:471.
  91. Finkelstein Y, Markowitz ME, Rosen JF. Low-level lead-induced neurotoxicity in children: an update on central nervous system effects. Brain Res Brain Res Rev 1998; 27:168.
  92. Bellinger D, Leviton A, Waternaux C, et al. Longitudinal analyses of prenatal and postnatal lead exposure and early cognitive development. N Engl J Med 1987; 316:1037.
  93. Schroeder SR, Hawk B, Otto DA, et al. Separating the effects of lead and social factors on IQ. Environ Res 1985; 38:144.
  94. Ruff HA, Bijur PE, Markowitz M, et al. Declining blood lead levels and cognitive changes in moderately lead-poisoned children. JAMA 1993; 269:1641.
  95. Soong WT, Chao KY, Jang CS, Wang JD. Long-term effect of increased lead absorption on intelligence of children. Arch Environ Health 1999; 54:297.
  96. Bellinger DC, Stiles KM, Needleman HL. Low-level lead exposure, intelligence and academic achievement: a long-term follow-up study. Pediatrics 1992; 90:855.
  97. Reuben A, Caspi A, Belsky DW, et al. Association of Childhood Blood Lead Levels With Cognitive Function and Socioeconomic Status at Age 38 Years and With IQ Change and Socioeconomic Mobility Between Childhood and Adulthood. JAMA 2017; 317:1244.
  98. Bellinger DC. Childhood Lead Exposure and Adult Outcomes. JAMA 2017; 317:1219.
  99. Searle AK, Baghurst PA, van Hooff M, et al. Tracing the long-term legacy of childhood lead exposure: a review of three decades of the port Pirie cohort study. Neurotoxicology 2014; 43:46.
  100. Koller K, Brown T, Spurgeon A, Levy L. Recent developments in low-level lead exposure and intellectual impairment in children. Environ Health Perspect 2004; 112:987.
  101. Ruff HA. Population-based data and the development of individual children: the case of low to moderate lead levels and intelligence. J Dev Behav Pediatr 1999; 20:42.
  102. Suarez CR, Black LE 3rd, Hurley RM. Elevated lead levels in a patient with sickle cell disease and inappropriate secretion of antidiuretic hormone. Pediatr Emerg Care 1992; 8:88.
  103. MYERSON RM, EISENHAUER JH. Atrioventricular conduction defects in lead poisoning. Am J Cardiol 1963; 11:409.
  104. Osman K, Pawlas K, Schütz A, et al. Lead exposure and hearing effects in children in Katowice, Poland. Environ Res 1999; 80:1.
  105. CHISOLM JJ Jr, HARRISON HE. The exposure of children to lead. Pediatrics 1956; 18:943.
  106. Erenberg G, Rinsler SS, Fish BG. Lead neuropathy and sickle cell disease. Pediatrics 1974; 54:438.
  107. Anku VD, Harris JW. Peripheral neuropathy and lead poisoning in a child with sickle-cell anemia. Case report and review of the literature. J Pediatr 1974; 85:337.
  108. Imbus CE, Warner J, Smith E, et al. Peripheral neuropathy in lead-intoxicated sickle cell patients. Muscle Nerve 1978; 1:168.
  109. Feldman RG, Hayes MK, Younes R, Aldrich FD. Lead neuropathy in adults and children. Arch Neurol 1977; 34:481.
  110. Schwartz J, Landrigan PJ, Feldman RG, et al. Threshold effect in lead-induced peripheral neuropathy. J Pediatr 1988; 112:12.
  111. Loghman-Adham M. Aminoaciduria and glycosuria following severe childhood lead poisoning. Pediatr Nephrol 1998; 12:218.
  112. Rosen JF, Chesney RW, Hamstra A, et al. Reduction in 1,25-dihydroxyvitamin D in children with increased lead absorption. N Engl J Med 1980; 302:1128.
  113. Lubran MM. Lead toxicity and heme biosynthesis. Ann Clin Lab Sci 1980; 10:402.
  114. Meredith PA, Moore MR, Goldberg A. Erythrocyte delta-aminolaevulinic acid dehydratase activity and blood protoporphyrin concentrations as indices of lead exposure and altered haem biosynthesis. Clin Sci (Lond) 1979; 56:61.
  115. Hammad TA, Sexton M, Langenberg P. Relationship between blood lead and dietary iron intake in preschool children. A cross-sectional study. Ann Epidemiol 1996; 6:30.
  116. Clark M, Royal J, Seeler R. Interaction of iron deficiency and lead and the hematologic findings in children with severe lead poisoning. Pediatrics 1988; 81:247.
  117. Bhambhani K, Aronow R. Lead poisoning and thalassemia trait or iron deficiency. The value of the red blood cell distribution width. Am J Dis Child 1990; 144:1231.
  118. Lewendon G, Kinra S, Nelder R, Cronin T. Should children with developmental and behavioural problems be routinely screened for lead? Arch Dis Child 2001; 85:286.
  119. Gordon RA, Roberts G, Amin Z, et al. Aggressive approach in the treatment of acute lead encephalopathy with an extraordinarily high concentration of lead. Arch Pediatr Adolesc Med 1998; 152:1100.
  120. Chisolm JJ Jr. The use of chelating agents in the treatment of acute and chronic lead intoxication in childhood. J Pediatr 1968; 73:1.
  121. Chisolm JJ Jr. The continuing hazard of lead exposure and its effects in children. Neurotoxicology 1984; 5:23.
  122. Soldin OP, Pezzullo JC, Hanak B, et al. Changing trends in the epidemiology of pediatric lead exposure: interrelationship of blood lead and ZPP concentrations and a comparison to the US population. Ther Drug Monit 2003; 25:415.
  123. Tehranifar P, Leighton J, Auchincloss AH, et al. Immigration and risk of childhood lead poisoning: findings from a case control study of New York City children. Am J Public Health 2008; 98:92.
  124. Geltman PL, Smock L, Cochran J. Trends in Elevated Blood Lead Levels Using 5 and 10 µg/dL Levels of Concern Among Refugee Children Resettled in Massachusetts, 1998-2015. Public Health Rep 2019; 134:608.
  125. Shakya S, Bhatta MP. Elevated Blood Lead Levels Among Resettled Refugee Children in Ohio, 2009-2016. Am J Public Health 2019; 109:912.
  126. Pezzi C, Lee D, Kennedy L, et al. Blood Lead Levels Among Resettled Refugee Children in Select US States, 2010-2014. Pediatrics 2019; 143.
  127. Parsons PJ, Reilly AA, Esernio-Jenssen D. Screening children exposed to lead: an assessment of the capillary blood lead fingerstick test. Clin Chem 1997; 43:302.
  128. Screening for elevated blood lead levels. American Academy of Pediatrics Committee on Environmental Health. Pediatrics 1998; 101:1072.
  129. Nakata H, Nakayama SMM, Yabe J, et al. Assessment of LeadCare® II analysis for testing of a wide range of blood lead levels in comparison with ICP-MS analysis. Chemosphere 2021; 271:129832.
  130. Carnahan B, Schaefer EW, Fogel BN. Point-of-Care Testing Improves Lead Screening Rates at 1- and 2-Year Well Visits. J Pediatr 2021; 233:206.
  131. Binns HJ, Campbell C, Brown MJ, Centers for Disease Control and Prevention Advisory Committee on Childhood Lead Poisoning Prevention. Interpreting and managing blood lead levels of less than 10 microg/dL in children and reducing childhood exposure to lead: recommendations of the Centers for Disease Control and Prevention Advisory Committee on Childhood Lead Poisoning Prevention. Pediatrics 2007; 120:e1285.
  132. Caldwell KL, Cheng PY, Jarrett JM, et al. Measurement Challenges at Low Blood Lead Levels. Pediatrics 2017; 140.
  133. Roberts, JR, Reigart, JR. Medical Assessment and Interventions. In: Managing Elevated Blood Lead Levels Among Young children: Recommendations from the Advisory Committee on Childhood Lead Poisoning Prevention. Centers for Disease Control and Prevention, Atlanta, GA, 2002.
  134. McElvaine MD, Orbach HG, Binder S, et al. Evaluation of the erythrocyte protoporphyrin test as a screen for elevated blood lead levels. J Pediatr 1991; 119:548.
  135. Porru S, Alessio L. The use of chelating agents in occupational lead poisoning. Occup Med (Lond) 1996; 46:41.
  136. Calello DP, Henretig FM. Lead. In: Goldfrank's Toxicologic Emergencies, 10th ed, Hoffman RS, Howland MA, Lewin NA, et al (Eds), McGraw Hill Education, New York 2015. p.1219.
  137. Shaltout AA, Ghawaby MM, Hassan MF, et al. High incidence of lead poisoning revealed by erythrocyte protoporphyrin (EPP) screening in Arabian children. Ann Trop Paediatr 1985; 5:207.
  138. Selbst SM, Henretig FM, Pearce J. Lead encephalopathy. A case report and review of management. Clin Pediatr (Phila) 1985; 24:280.
  139. Jones A. Emerging aspects of assessing lead poisoning in childhood. Emerg Health Threats J 2009; 2:e3.
  140. Martin CJ, Werntz CL 3rd, Ducatman AM. The interpretation of zinc protoporphyrin changes in lead intoxication: a case report and review of the literature. Occup Med (Lond) 2004; 54:587.
  141. Schwartz BS, Caffo B, Stewart WF, et al. Evaluation of cumulative lead dose and longitudinal changes in structural magnetic resonance imaging in former organolead workers. J Occup Environ Med 2010; 52:407.
Topic 6491 Version 38.0

References

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