For centuries, lead toxicity has been one of the most significant preventable causes of neurologic morbidity from an environmental toxin. A heavy metal, lead is ubiquitous in our environment but has no physiologic role in biological systems. Lead toxicity is a particularly insidious hazard with the potential of causing irreversible health effects. It interferes with a number of body functions primarily affecting the central nervous, hematopoietic, hepatic and renal system producing serious disorders. Acute toxicity is related to occupational exposure and is quite uncommon. Chronic toxicity on the other hand is much more common. Research on the effects of lead on adults has prompted the suggestion that acceptable levels of lead in adults be dropped almost to those of children. 
The ongoing emphasis on abatement of lead environments places added emphasis on occupational exposure to lead (eg, among workers at smelters or battery recycling plants).  Such exposure is a continuing problem. Whereas occupational exposure remains an occasional concern, the greatest public health issue related to lead at present is exposure of young children to decaying fragments of leaded paint.
Pediatric lead poisoning
Compared with adult lead poisoning, pediatric lead poisoning is a somewhat newer problem. First reported in the late 1800s in Australia, interest in childhood lead poisoning and its manifold clinical presentations has burgeoned. It should be noted that toxic metals, including lead, can be transmitted from a mother to her child via breast milk. 
Lead poisoning is probably the most important chronic environmental illness affecting modern children. Despite efforts to control it and despite apparent success in decreasing incidence, serious cases of lead poisoning still appear in hospital emergency departments (EDs), clinics, and private physicians’ offices.
In children, virtually no organ system is immune to the effects of lead poisoning. Perhaps the organ of most concern is the developing brain. Any disorganizing influence that affects an individual at a critical time in development is likely to have long-lasting effects. Such is the effect of lead on the developing brain. Effects on the brain appear to continue into the teenaged years and beyond. A high index of suspicion is necessary for physicians treating pediatric patients.
The major mechanism of lead toxicity is due to increased generation of reactive oxygen species (ROS) and interference with generation of antioxidants. Lead causes the generation of ROS like hydroperoxide, hydrogen peroxide, and singlet oxygen. ROS are stabilized by glutathione in the body. Ninety percent of glutathione in the cell exists in reduced form and 10% in oxidative form, and it typically acts as an antioxidant defense mechanism. Glutathione stabilizes ROS, and after being converted (oxidizing) to glutathione disulfide, it is reduced back to GSH by glutathione reductase. Lead inactivates glutathione by binding to GSH’s sulfhydryl group, which causes GSH replenishment to become inefficient, thereby increasing oxidative stress. Lead also interferes with the activity of other antioxidant enzymes including superoxide dismutase and catalase. The increase in oxidative stress leads to cell membrane damage due to lipid peroxidation. Lead blocks the activity of 5-aminolevulinic acid dehydratase and leads to hemoglobin oxidation, which along with the lipid peroxidation can result in red cell hemolysis. 
Lead entering the intravascular space binds quickly to red blood cells. Lead has a half-life of approximately 30 days in the blood, from where it diffuses into the soft tissues, including the kidneys, brain, liver, and bone marrow.
Lead then diffuses into bone and is stored there for a period that corresponds to a half-life of several decades. Increased bone turnover with pregnancy, menopause, lactation, or immobilization can increase blood lead levels. Estimations of blood lead levels are more useful for diagnosing acute lead poisoning, whereas the extent of past lead exposure can be estimated by determining the body burden of lead on the basis of results from the edetate (EDTA) calcium disodium (CaNa2 EDTA) lead mobilization test.
Lead is primarily excreted in urine and bile, but the elimination rate varies, depending on the tissue that absorbed the lead. The kidney excretes lead by means of glomerular filtration and tubular secretion. Lead has bidirectional transport across the tubular epithelium. The clearance of lead ranges from 1 to 3 mL/min and is relatively independent of kidney function.
The effects of lead poisoning on the brain are manifold and include delayed or reversed development, permanent learning disabilities, seizures, coma, and even death. The long-term effect of lead exposure is maximal during the first 2 or 3 years of life, when the developing brain is in a critical formative stage.
The most significant lead exposure in adults usually occurs at the workplace, whereas for children, other forms of environmental exposure are more important. Although lead toxicity can occur after a single event, it is usually a result of chronic exposure.
Sites and occupations associated with lead exposure include pipe cutting, lead mining and ore crushing, lead and copper smelting, welding operations, construction, the rubber industry, the plastic industry, radiator repair, battery manufacturing, soldering of lead products, the printing industry, glass manufacture, organic lead production, solid waste combustion, frit manufacture, and paint and pigment manufacture. Persons employed in these occupations may also expose family members to lead by transporting lead dust from the workplace to their homes.
Other environmental exposure
Exposure from lead-based paint was significant among children in the past. Although lead was banned from use in residential paint, it continues to be used in nonresidential settings, and as a result of its past use, lead paint can still be found in many older homes.
Leaded gasoline contaminates the atmosphere. Although lead has been removed from gasoline in Western countries, leaded gasoline continues to be used in the developing world. Huffing of leaded gasoline (ie, deeply inhaling fumes to achieve a “high”) could also cause poisoning.
Food has been an important source of lead exposure. Surface contamination of homegrown vegetables, storage cans with lead solder seams (banned in 1991), and kitchenware are sources of lead contamination in food. Strong animal evidence suggests that malnutrition is highly significantly associated with increased levels of blood lead. 
Water remains an important source of lead poisoning because lead from the atmosphere contaminates bodies of water.  The nature of plumbing also may be important in this regard. Although use of lead pipes (largely replaced by copper or polyvinyl pipes) has declined considerably since the 1950s, old public water systems continue to have networks that include lead piping. Because the use of lead-based soldering of copper pipes was permitted until 1986, homes with copper plumbing may have substantial lead in the water. In May 2015, at least 28 children under the age of five have been killed by drinking stream water contaminated with lead in Nigeria's Niger state. 
Some hobbies are associated with exposures to lead. These hobbies may include making bullets, making fishing-weights, soldering, indoor firearm shooting, and remodeling older homes.
Soil contaminated with lead, such as may be found surrounding lead smelters and in homes from deterioration of exterior surfaces, can be an important source of lead exposure.
Moonshine ethanol (ie, illegally distilled corn whiskey) made in lead-containing vessels, such as discarded automobile radiators, has been associated with lead poisoning and even local epidemics. 
Topical agents that contain lead, such as kohl and surma, may be ingested accidentally.
Several reports exist of lead poisoning that develops as the result of absorption of lead from retained bullet or shrapnel fragments. Bullets located in areas bathed by fluids are more likely to dissolve, while those embedded in soft tissues are likely to be walled off by inflammation.
An incidental finding of bullet or shrapnel fragments on an x-ray should prompt consideration of possible elevated lead levels, though most of these cases occur only with intra-articular fragments. Of particular concern is a retained bullet in the spine, an area where removal is often considered too dangerous to attempt. 
Frequently, 1 or 2 children in a family develop more lead poisoning than other siblings. This observation may be related to age, activity, or genetics. Identical twins seem to have concordant lead levels and biologic evidence of lead’s effects, but this is less likely to be the case with fraternal twins.
For further information on etiology, see Pathophysiology and Etiology of Lead Toxicity.
United States statistics
Lead poisoning is said to be the most common environmental illness of children in the United States. The incidence varies with age, socioeconomic status, the population of a given community, race, and the age of the home.
Although no blood level of lead is considered safe, the Centers for Disease Control and Prevention (CDC) has established 10 µg/dL as the level of concern. Approximately 9% of children aged 1-5 years have blood levels higher than 10 µg/dL. Because low socioeconomic status is also a risk factor for lead exposure, children in inner cities are at highest risk. In some rural areas of the United States, 20% of children have been reported to have levels higher than 10 µg/dL. 
Lead poisoning occurs in every group, and only the frequency varies; it is not just a disease of black inner-city children. According to the 1997 National Health and Nutrition Examination Survey (NHANES), 16.4% of children living in cities with more than 1 million people and in homes built before 1946 have elevated lead levels.
Of interest is the remarkable decrease in the prevalence of elevated lead levels in children in the 1999-2004 time frame as compared with the 1988-1991 time frame. According to the NHANES data, the prevalence of children with lead levels over 10 µg/dL was 8.4% in 1988-1991 but only 1.4% in 1999-2004, representing an 84% decline.  levels continue to be highest among non-Hispanic black children, Mexican American, and non-Hispanic white children, with the greatest risk being in the non-Hispanic black population.
Generally, adults develop lead poisoning as the result of an occupational exposure or from exposure through a hobby. Several states cooperate in the SENSOR program, which monitors lead exposure in adults from occupational sources.
According to a report from the CDC’s Adult Blood Lead Epidemiology and Surveillance (ABLES) program, the incidence of BLLs of 25 µg/dL or higher in adults (persons aged 16 years or older) declined nationally from 14.0/100,000 in 1994 to 6.4/100,000 in 2011.  (Although BLLs lower than 40 µg/dL have been considered acceptable in adults, research data have raised concerns about the effects of low-level lead exposure.)
The highest numbers of workers exposed to lead with BLLs of 25 µg/dL or greater included employees in the storage battery manufacturing and lead and zinc ore mining industries, according to the ABLES report. 
Lead poisoning has been reported in almost every country on earth. Blood lead levels are higher in developing countries because of continued use or later phaseout of leaded gasoline and paint. Occupational exposure in these countries is higher as well. In particular, the old “iron-curtain” countries had less strict guidelines for occupational and environmental exposures than other places in the world; thus, exposures there were common.
A Swedish study by Evans et al, which reported on 926 patients with incident severe CKD and 998 controls with a 7- to 9-year follow-up, suggested that low-level exposure to lead may not cause an increased risk of severe chronic kidney disease (CKD).  However, the authors cautioned that because only native Swedes were used in their study, the generalizability of the data may be limited; they also noted that whereas an expert rating method was used to assess lead exposure, BLLs were not measured to confirm the rating method’s validity. 
Young children who are independently mobile are at greatest neurologic risk from chronic exposure to low or moderate levels of lead. From the time children are able to crawl until they enter school, they are at risk of ingesting lead-containing dust. Although this sometimes is associated with pica and intentional ingestion of paint chips, lead poisoning often occurs without such behavior. Children may also be at risk for lead toxicity if folk remedies are used or if their parents, siblings, or caregivers are involved in lead-related occupations.
Children younger than 3 years are at the greatest risk for lead poisoning. This is because these children are most likely to put things containing lead into their mouths and because their brains are rapidly developing and are most vulnerable to any disorganizing influence. However, physicians and other health care professionals must be aware that lead poisoning can occur in children of any age.
Adults are now believed to be affected at a lower level of exposure than was once assumed. This has sparked renewed interest in occupational exposure to lead and its consequences. Careful attention must be paid to the occupations of adults who present with uncommon peculiar symptoms and signs.
Because of occupational exposures, men have higher lead levels than women. No sex difference in incidence is reported in children.
Racial differences in incidence
Although no compelling evidence exists that any particular race is biologically predisposed to lead toxicity, covariant conditions such as poor nutrition and lower socioeconomic status clearly are associated with chronic lead poisoning.
Certain populations, such as African American children and new immigrants living in homes with decaying lead-based paint in low-income urban centers, are at increased risk of lead poisoning. The NHANES III data have shown higher lead levels among non-Hispanic blacks and Mexican Americans. Whether this translates into a higher incidence of lead nephropathy among these persons is not known.
Overall, black non-Hispanic children appear to have the greatest risk of developing lead poisoning. The NHANES figures for 1997 reveal a prevalence rate of 21.9% among black non-Hispanic children living in homes built before 1946, a rate of 13.7% in those living in homes built in 1946-1973, and a rate of 3.4% in those living in homes built subsequent to 1973.
This compares to a prevalence of 13%, 2.3%, and 1.6% among Mexican-American children and 5.6%, 1.4%, and 1.5% among white non-Hispanic children living in homes built before 1946, living in homes built in 1946-1973, and living in homes built subsequent to 1973, respectively.
An analysis of trends in blood lead levels over the past 20 years shows that, although the overall geometric mean blood lead level in children has dropped dramatically, disparities still exist, causing increased risk to certain populations. The factors of living in older housing, poverty, age, and being non-Hispanic black places a child at risk for elevated blood lead levels. 
Essentially, 2 syndromes of lead poisoning exist, depending on exposure: one syndrome is associated with acute or subacute high-level lead exposure, and the other is associated with chronic low-level lead exposure.
With exposure to high levels of lead, patients develop lethargy, progressing to coma and seizures. Death is uncommon with appropriate medical management. Long-term sequelae depend on the duration, as well as the amount, of exposure. Acute lead nephropathy is usually completely reversible with chelation therapy. Deaths may result from the elevated intracranial pressure (ICP) associated with lead encephalopathy.
With chronic exposure to low or moderate levels of lead, subacute symptoms develop. Patients with chronic lead nephropathy may have a progressive decline in kidney function and eventually require renal replacement therapy.
Mortality related to lead toxicity is rare today. However, morbidity remains common. Because lead is an enzymatic poison, it perturbs multiple essential bodily functions, producing a wide array of symptoms and signs.
Adults generally do not develop central effects but may develop distal motor neuropathies. Some reports document an increase in depressive disorders, aggressive behavior, and other maladaptive affective disorders in adult patients with lead poisoning. Men with lead poisoning tend to have lower sperm counts and may experience frank impotence; women have an increase in miscarriages and smaller babies.
In the pediatric population, fatalities associated with lead encephalopathy were reported in the 1960s. Today, with aggressive management of ICP, these deaths are preventable. Occasional cases of acute lead encephalopathy still occur, and these often result in severe neurologic damage. Mounting evidence suggests that lead poisoning in childhood produces a long-term problem with learning, intelligence, and earning power. Asymptomatic lead poisoning has a far better prognosis.
In cooperation with local health departments, the physician should educate families about the following:
Causes and effects of lead poisoning
Relationship between blood lead level and anticipated medical or neuropsychological problems
Importance of follow-up or serial blood lead level determinations to monitor effects of treatment and environmental lead abatement
Identifying and eliminating possible sources of lead exposure
Increased lead absorption in patients with iron-deficiency anemia
Local resources about lead exposure and treatment
All patients must be educated in lead avoidance. The termination of exposure to lead is imperative. In particular, workers should be educated regarding the health risks of lead and sources that may cause poisoning.
A good, substantial diet is important; lead absorption is increased when a diet rich in fats is consumed. Also, diets low in iron, calcium, and vitamin C increase the likelihood of lead absorption and resultant lead poisoning. Dietary fiber helps promote good peristalsis and decreases the opportunity for lead absorption; thus, at least 15 g of dietary fiber is suggested for children each day.
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